Upload
others
View
2
Download
0
Embed Size (px)
Citation preview
i
CAPTIVE REARING AND SEMIOCHEMCIAL ECOLOGY OF TRICHOGRAMMA
PAPILIONIS (HYMENOPTERA: TRICHOGRAMMATIDAE)
A DISSERTATION SUBMITTED TO THE
GRADUTE DIVISION OF THE UNIVERSITY OF HAWAIʻI AT MĀNOA IN
PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF
DOCTOR IN PHILOSOPHY
IN
ENTOMOLOGY
MAY 2020
BY
ABDULLA N. ALI
DISSERTATION COMMITTEE:
MARK G. WRIGHT, CHAIRPERSON
JON- PAUL BINGHAM (UNIVERSITY REP)
LEYLA KAUFMAN
PETER FOLLETT
GORDON BENNETT
i
Ó copyright 2020
By
Abdulla N. Ali
ii
DEDICATION
At first dedicating this dissertation to Almighty Allah, without his mercy and sympathy, I was
not able to accomplish this study. Almighty Allah gave me the power and confidence to done
project work and also holy prophet Muhammed and his family (Peace Be Upon Them) who are a
light for my life. I also dedicate this dissertation to my lovely parents with the deepest gratitude
whose love and prayers have always been a source of strength for me. To my father who did not
live long enough to see me complete this successful mission.
My dedicated also goes to my lovely wife Maha and my children Wisam and Taim who fill my
heart with hope and happiness. To my siblings and friends, their continuous support and advice
have helped me to pursue my goals.
iii
ACKNOWLEDGMENTS
Apart from my efforts, the success of my project depends largely on the encouragement
and guidelines of many others. I take this opportunity to express my gratitude towards them.
First of all, I would like to thank my major professor Dr. Mark G. Wright for his continual and
valuable guidance, huge support that I believe without his supervision I would not finish any of
my research. It is not enough to express myself for all the great things he has done to me. Dr.
Wright is more than an advisor. I have to be humble with all the things I learned from him in his
laboratory. I learned from him how to be a professional; how do I think critically and link ideas.
I would like to express my serious thank you to my dissertation committee members, Drs. Leyla
Kaufman, Jon-Paul Bingham, Peter Follett, and Gordon Bennett. I appreciate all thoughtful
feedback and criticism of my chapters that were very deliberate and directed me through my
Ph.D. study. I am truly thankful for all useful inputs. My family (Mom, Dad, brothers and
sisters). To my sweetheart wife Maha A. Najm and my kids (Wisam and Taim Ali), my depth
thank you to you all for your prayers and immersive support. Thank you Maha for being very
penitent and genuinely supportive to me. Thank you for giving me such a beautiful gift (Wisam
and Taim). I would also like to thank the Ministry of Higher Education & Scientific Research,
University of Kufa, Iraq for granting me a scholarship and an opportunity to study abroad. Iraqi
cultural office in Washington D.C., they are appreciated for their genuine support and financial
aid through five and a half year.
To my all student colleagues, it was such a blessing time to be with you. I am indebted to
David Honsberger for his assistance with fields work, critical reading and editing on the first
drafts of my thesis manuscripts. Finally, it is my pleasure to be indebted to all people who
believed in me and supported me even without my awareness. There are definitely many people
iv
whose names have not mentioned, helped me to accomplish this important mission in my life.
This work was funded by Hatch Project 919-H, administered by CTAHR, and the Ministry of
Higher Education & Scientific Research, University of Kufa, provided support to me.
v
LIST OF PUBLICATIONS
Ali, A.N. and Wright, M.G. 2020. Behavior response of Trichogramma papilionis in response to
host eggs, host plants, and induced plant cues. Biological Control. (Accepted)
Ali, A.N. and Wright, M.G. Fitness effects of founder female number of Trichogramma
papilionis reared on a factituous host Ephestia kuehniella (Zeller). Proceedings of the Hawaiian
Entomological Society (In review)
Ali, A.N. and Wright, M.G. 2018. Response of Trichogramma papilionis to plant volatiles
associated with Lepidoptera oviposition. Biological Control in Pest management Systems of
Plants Annual Meeting. Whitefish, Montana, October 2018. (Oral presentation)
Papers in Preparation:
Ali, A.N. and Wright, M.G. Response of Trichogramma papilionis wasps to blends of synthetic
semiochemicals.
Ali, A.N. and Wright, M.G. The effect of plant derived semiochemicals on searching behavior of
Trichogramma papilionis in different environments.
vi
ABSTRACT
This study addressed aspects of mass rearing of Trichogramma papilionis (Hymenoptera;
Trichogrammatidae), including the effects of varied colony founder size on wasp fitness, and the
exploitation of the wasps to locate egg hosts in which to deposit thereof progeny. Effects of
initial founder female number of T. papilionis were investigated using fitness parameters
(emergency rate, sex ratio and fecundity) to quantify the effects of a severe bottleneck (single
founder female) on 10 subsequent generations. Results showed that no significant difference for
eggs laid per female over ten generations, suggesting that the imposed bottleneck did not result
in reduced female fecundity for any founder population size. However, founder numbers did
affect both the emergence rate and sex ratio of T. papilionis. Further investigation of the impacts
of inbreeding on field performance of the wasps was discontinued as extremely limited host
finding ability of the wasps was observed in some habitats. The emphasis of the work was thus
shifted to elucidating the searching behaviors of T. papilionis in relation to chemical cues. The
hypothesis that T. papilionis are attracted to host habitat by host plant or egg-associated volatile
chemicals was tested.
The response of T. papilionis females to olfactory cues from host eggs, host plants and
induced plant volatiles were studied. The response of T. papilionis females to different info-
chemical cues was tested in Y-tube olfactory assays. Wasps made a positive response to odors
from corn earworm (CEW) eggs Helicoverpa zea (Lepidoptera: Noctuidae) compared with blank
air, while there was a negative response to Ephestia kuehniella eggs (Lepidoptera: Pyralidae)
compared blank air: T. papilionis females thus preferred odors from corn earworm eggs over the
Mediterranean flour moth eggs. Further, the wasps were attracted to volatile emissions from sunn
hemp Crotalaria juncea (L.) over maize Zea mays (L.), despite both plants infested with H. zea
vii
eggs. No preference was observed for plants not infested with H. zea eggs, suggesting T.
papilionis showed a positive response to stimuli from sunn hemp plants that might be induced by
H. zea oviposition. Chemical volatile collection and headspace analysis was conducted.
Headspace analysis and thermal desorption and gas chromatography–mass spectrometry (TD-
GCMS) was used to qualitatively and semi-quantitatively determine the difference in plant
volatile organic components (VOCs) from Helicoverpa zea egg infested sunn hemp plants
compared with intact sunn hemp plants and H. zea eggs only. TD is used as a preconcentration
technique of VOCs for gas chromatography-mass spectrometry (GC–MS), making it useful to
detect low-concentration analytes that would otherwise be undetectable. Results demonstrated
that sunn hemp plants released 55 chemical volatiles with five compounds that were unique, or
were emitted in higher concentrations, for plants infested with CEW eggs. These volatile
compounds were consistent with linear alkanes, aldehydes, aromatics, polyterpene-related
compounds, naphthalene derivatives, and ester-related compounds. High concentrations of
anisole, β-myrcene, cis-butyric acid, trans-isoeugenol, and bis(2-ethylhexyl) phthalate were
found in infested sunn hemp. The majority of GCMS peaks detected from H. zea eggs were
consistent with phosphates, pheromone-related compounds, various natural products, a series of
glycol-related compounds, and a series of fatty acid ester-related compounds. Several
compounds were shared in sunn hemp samples and corn earworm eggs: anisole, β-myrcene, and
bis (2-ethylhexyl) phthalate, but were detected in higher concentrations from the plants with H.
zea eggs.
Evaluation of the response and the performance of T. papilionis females in y-tube
olfactory bioassays to single compounds, and blends of synthetic chemical showed that the
wasps were significantly attracted to only two of the assayed chemical volatiles (anisole and
viii
bis(2-ethylhexyl) phthalate). Some concentrations of anisole and bis (2-ethylhexyl) phthalate
were attractant to the wasps, whereas some concentrations of the other tested chemical
compounds repelled the wasps. Wasps were attracted to a blend of anisole and bis(2-ethylhexyl)
phthalate (25μL /100μL ratio) which is similar to the ratio of anisole to bis(2-ethylhexyl)
phthalate detected in the (GC-DMS) chromatograph for C. juncea plants infested with H. zea
eggs. No significant attraction to any other blend ratios of anisole and bis(2-ethylhexyl) phthalate
was observed.
Greenhouse and field experiments were conducted to determine whether the patterns
observed in the y-olfactometer were consistent under less constrained conditions. The optimal
blend identified above was initially tested in a greenhouse, and later in closed-canopy
environments (under trees) and open habitat with no trees. The parasitism rate by T. papilionis
wasps was significantly increased when the wasps were exposed to anisole and bis(2-ethylhexyl)
phthalate blend in both greenhouse and outdoor trials (covered habitat), at least over short
distance (up to 2m from the volatile sources).
The findings presented in this dissertation underscore the importance of improving our
understanding of how tri-trophic interactions (natural enemies- herbivores and host plants)
interact to influence insect behavior, as well as the impact of variable environments, impact
parasitoid wasps. The results may also contribute to finding a way to improve natural enemy
efficacy in augmentative and conservation biocontrol efforts. Semiochemical cues can positively
or negatively affect the response of parasitic wasps. This may provide an understanding of
ecology that could facilitate achieving successful field parasitism and thus enhanced pest
management.
ix
TABLE OF CONTENTS
ACKNOWLEDGMENTS……………………………………………………………..................iii
LIST OF PUBLICATIO........................................…………………………………......................v
ABSTRACT...................................................................................................................................vi
LIST OF TABLES…………………………………………………………………....................xiv
LIST OF FIGURES…………………………………………………………………...................xv
LIST OF ABBREVIATIONS.....................................................................................................xvii
CHAPTER 1: GENERAL INTRODUCTION AND DISSERTATION STRUCTUR...................1
1.1 Background ……………………………………………………………………..................... 1
1.2 Aims of this dissertation...........................................................................................................4
1.3 Dissertation organization..........................................................................................................5
References........................................................................................................................................7
CHAPTER 2: FITNESS EFFECTS OF FOUNDER FEMALE NUMBER OF
TRICHOGRAMMA PAPILIONIS REARED ON A FACTITIUOS HOST EPHESTIA
KUEHIELLA (ZELLE)..................................................................................................................11
Abstract…………………………………………………………………………………..............11
2.1 Introduction………………………………………………………………………..................12
2.2 Materials and Methods ……………………………………………………………................16
2.2.1 Egg parasitoid colony...............................................................................................16
2.2.2 Experimental population...........................................................................................16
2.2.2.1 Evaluation of the effects of number of founder females.........................................16
2.2.2.2 Establishing isofemales and other lines.................................................................17
x
2.2.2.3 Evaluating fitness-proxies of the founder females over successive
generations.........................................................................................................................18
2.2.3 Statistical analyses...................................................................................................19
2.3 Results……………………………………………………………………….........................20
2.3.1 Fitness measures of Trichogramma papilionis.............................................20
2.3.2 Response of emergence rate..........................................................................22
2.3.3 The response of sex ratio..............................................................................24
2.3.4 The response of parasitized eggs per female................................................25
2.4 Discussion................................................................................................................................28
2.4.1 Variability among the fitness parameters.....................................................28
Conclusion.............................................................................................................31
References……………………...…………………………….......................................................32
CHAPTER 3: SEARCHING BEHAVOR OF TRICHGRAMMA PAPILIONIS IN RESPONSE
TO HOST EGGS, HOST PLANTS, AND INDUCED PLANT
CUES……………………………………………….....................................................................41
Abstract…………...……………………………….......................................................................41
3.1 Introduction………………………………………………………………………..................42
3.2 Materials and Methods……………………………………………………………….............45
3.2.1 Behavioral response of parasitoids……………………………………......45
3.2.2 Dynamic Y-tube olfactory bioassays……………………………………….45
3.2.3 Plants and Insects……………………………………………….................48
3.2.4 Egg deposition experiments…………………………………………….….49
3.2.4.1 Egg-infested plants……………………………………………….............49
xi
3.2.4.2 Helicoverpa zea and Ephestia kuehniella eggs………………………….50
3.2.5 Trichogramma wasps………………………………………………............50
3.2.6 Volatile collection and headspace analysis..................................................51
3.2.7 Statistical analysis………………………………………………................53
3.3. Results………………………………………………………………………….....................53
3.3.1 H. zea and E. kuehneilla eggs versus blank air…………………................53
3.3.2 H. zea eggs versus E. kuehneilla eggs…………………………………......54
3.3.3 H. zea egg-infested sunn hemp plant and maize plant versus uninfested
plant……………………………………...............................................................54
3.3.4 H. zea egg-infested sunn hemp versus H. zea egg-infested maize…………54
3.3.5 Headspace volatile collection from sunn hemp plants.................................56
3.3.6 Dynamic headspace analysis of H. zea eggs................................................57
3.4 Discussion................................................................................................................................60
3.4.1 Response of T. papilionis female wasps to egg hosts………………………60
3.4.2 Response of T. papilionis to plant volatiles……………………………......61
Conclusion………………………………………..................................................63
References.....................................................................................................................................64
CHAPTER 4: RESPONSE OF TRICHOGRAMMA PAPILIONIS WASPS TO BLENDS OF
SYNTHETIC SEMIOCHEMICALS.............................................................................................71
Abstract…………………………………………………………………………………..............71
4.1 Introduction………………………………………………………………………..................72
4.2 Materials and Methods………………………………………………………….....................75
4.2.1 Test insects ...................................................................................................75
xii
4.2.2 Y-tube olfactometer bioassays......................................................................75
4.2.3 Compounds of interest .................................................................................75
4.2.4 Tests of Trichogramma response to volatile compounds..............................79
4.2.5 Statistical analysis .......................................................................................81
4.3. Results……………………………………………………………………….........................81
4.3.1 Response of Trichogramma wasps to volatile compounds...........................81
4.4. Discussion………………………………………………………………………...................85
Conclusion.............................................................................................................88
References .....................................................................................................................................89
CHAPTER 5: THE EFFECT OF PLANT DERIVED SEMIOCHEMICALS ON SEARCHING
BEHAVIOR OF TRICHOGRAMMA PAPILONIS IN DIFFERENT
ENVIRONMENTS........................................................................................................................99
Abstract……………………………………………………..........................................................99
5.1 Introduction………………………………………………………………………................100
5.2 Materials and Methods………………………………………………………………...........102
5.2.1 Trichogramma wasp culture.......................................................................102
5.2.2 Single volatile chemical trial: Preliminary Field experiments...................102
5.2.3 Greenhouse experiments.............................................................................103
5.2.4 Open field optimal volatile blend trial........................................................104
5.2.5 Open and covered habitat optimal volatile blend trial...............................105
5.2.6 Statistical analysis......................................................................................105
5.3 Results……………………………………...........................................................................106
5.4 Discussion……………………………………………………………..................................110
xiii
Conclusion...........................................................................................................113
References....................................................................................................................................114
CHAPTER 6: GENERAL CONCLUSTION AND RECOMMENDATIONS...........................118
6.1 General Conclusions...............................................................................................................118
6.2 Recommendations and further works....................................................................................122
References....................................................................................................................................123
Appendices...................................................................................................................................124
Appendix A. Summary of the major peaks (VOCs) emitted by sunn hemp plant in
response to H. zea egg-deposition (Treatment) and healthy sunn hemp plant
(Control)....................................................................................................................124
Appendix B. Summary of DMS result for corn earworm Helicoverpa zea eggs and a
control blank..............................................................................................................130
Appendix C. A brief summary literature overview of the chemical compounds tested in
Chapter 4, emphasizing interactions with various insects. Citations were obtained
from Web of Science®, searching for the specific compound in association with
insects. The biological origin (plant or insect) and functional activity (in insects) for
each are summarized..................................................................................................136
xiv
LIST OF TABLES
Table 2.1. Analysis of variance of Trichogramma papilionis fitness parameters as affected by
founder population and environmental conditions (25°C vs 22°C) over 10
successive generations in captivity. Laboratory line: 22 ± 2ºC, 60 –70% RH, LD
16:8 h. photoperiod. Mass-rearing line: 25 ± 1ºC, 75-88% RH, LD 16:8 h.
photoperiod. * Indicates a significant effect, P < 0.050, LSD
test.….....................................................................................................................21
Table 3.1. Summary of volatile chemicals collected, showing the compounds with the largest
peaks, from corn earworm eggs, corn earworm infested sunn hemp plant, and
healthy sunn hemp plants. (+) = Present; (-) = Not present...................................59
xv
LIST OF FIGURES
Fig. 2.1. Response (Mean ± SEM) in the emergence rate of three founder population sizes (1, 2,
and 10 founder females) of Trichogramma papilionis over ten serially bottlenecked
generations. Treatments not connected by the same letter were significantly
different......................................................................................................................22
Fig. 2.2. Coefficient of variation in the emergence rate of Trichogramma papilionis from three
founder population sizes (1, 2, 10 females) over ten generations..............................23
Fig. 2.3. Trichogramma papilionis sex ratios of progeny from three founder female treatments
(1, 2, and 10 founder females). Values are estimated mean (± SEM). Bars not connected by the
same letter are significantly different............................................................................................24
Fig. 2.4. Mean estimates (± SEM) of the sex ratio of Trichogramma papilionis in two
experimental lines (22°C, L- line, and 25°C, M- line). Treatments not connected by
the same letter were significantly different................................................................25
Fig. 2.5. Mean (± SEM) number of Ephestia eggs parasitized per Trichogramma papilionis
female for the three founder treatments (1, 2 and 10 founder females). Bars not
connected by the same letter are significantly different.............................................26
Fig. 2.6. Coefficient of variation in percentage parasitized Ephestia eggs for three different
founder population size colonies (1, 2, and 10 founder females) of Trichogramma
papilionis over 10 successive generations..................................................................27
Fig. 3.1. A schematic representation of a Y-tube olfactometer apparatus illustrating the direction
of airflow, odor sources, and site of introduction of the study animals. This figure is
adapted from http://www.chromforum.org..................................................................48
xvi
Fig. 3.2. Response of Trichogramma papilionis females to various olfactory cues in a y-tube
olfactometer. A: H. zea eggs and E. kuehneilla eggs vs. Blank air; ** significant positive
response to H. zea eggs vs. blank air (Fisher’s exact test p = 0.012), non-significant
Fisher’s exact test p = 0.10; B: to H. zea eggs vs. E. Kuehneilla eggs; ** Fisher’s exact
test p = 0.002; C: to H. zea egg-infested sunn hemp vs. intact sunn hemp (control), and
egg-infested maize vs. intact maize (control); ** Fisher’s exact test p = 0.001, p = 0.020;
D: to H. zea egg-infested sunn hemp vs. H. zea egg-infested maize; ** Fisher's exact test
p = 0.006..............................................................................................................................55
Fig. 3.3. Overlay of DMS chromatograms of Control (blue), Treatment (green), and a control
blank (red). Numbers in parentheses above peaks identify compounds (see Table 3)
that were identified to be a special interest..................................................................57
Fig. 3.4. Overlay of DMS chromatograms of corn earworm eggs and a control blank. Overlay of
DMS chromatograms of corn earworm eggs and a control blank. Numbers in
parentheses above peaks identify compounds (see Table 3) ......................................58
Fig. 4.1. Olfactory behavioral response of Trichogramma papilionis females in a y-tube
olfactometer bioassay to select volatile compounds, measured as the percentage of
wasps choosing the chemical cue over the control. The difference of the insects
choosing an odor was determined by a χ2 goodness of fit test. ** = significant at a =
0.05 and ns = non- significant......................................................................................82
xvi
Fig. 4.2 Percentage response of Trichogramma papilionis females to different ratios of
semiochemical volatiles in a y-tube olfactometer to select volatile compounds,
measured as the percentage of wasps choosing the chemical cue over the
control. ** = significant preference for treatment over control at a = 0.05, χ2
goodness of fit tests. Bars without connectors were not significantly different
for positive responses to the cues.....................................................................83
Fig. 4.3. The percentage positive response of female Trichogramma papilionis wasps to a
range of blend ratios of volatile compounds in a y-tube olfactometer to select
volatile compounds, measured as the percentage of wasps choosing the
chemical cue over the control. ** = significant, a = 0.05 and ns = non-
significant response, χ2 goodness of fit tests....................................................84
Fig. 5.1. Mean parasitism rate (±SEM) by Trichogramma papilionis in cornfields
comparing anisole as an attractant, to untreated release plots
(p = 0.092) ..................................................................................................106
Fig. 5.2. Parasitism rate of Trichogramma papilionis from the greenhouse (mean ±SEM),
with and without chemical attractants (anisole + bis(2-ethylhexyl) phthalate),
and over a distance of up to 6m; a) overall percentage of parasitism; b)
percentage parasitism at different distances from the release point, treatment
and control.....................................................................................................108
Fig. 5.3. Mean parasitism rate (±SEM) by Trichogramma papilionis: a) open habitat b).
covered and open habitat) comparing the optimal blend (anisole + bis(2-
ethylhexyl) phthalate) as an attractant, to untreated release trial. ** significant
at a = 0.05 and ns = non- significant.............................................................109
xvii
LIST OF ABBREVIATIONS
L line, Laboratory line; M line, Mass-rearing room line; CEW, corn earworm moth
Helicoverpa zea; GC-DMS chromatography, Desorption Gas Chromatography Mass
Spectrometry. UGC, urban garden center; UH campus, University of Hawaiʻi at Mānoa
campus. Ani, anisole; Bis, bis(2-ethylhexyl) phthalate.
1
CHAPTER 1
GENERAL INTRODUCTION AND DISSERTATION STRUCTURE
1.1 Background
Egg parasitoids are extensively used in biological control programs. Their impact in
suppressing pests is expected to be realized by decreasing the number of emerging larvae
(van Lenetern, 2003). The genus Trichogramma (Hymenoptera: Trichogrammatidae)
contains a wide range of species that are widely applied and studied natural enemies
because they are used in augmentative biological control, albeit with varying degrees of
success (Bueno et al., 2009; Smith, 1996). Trichogramma spp. are used to target
lepidopteran pests (Suckling and Brockerhoff, 2010), since they can be mass-produced
inexpensively and released at inundative densities in crop systems (Mansour, 2010;
Chailleux et al., 2012). Many species (e.g., T. pretiosum, T. ostriniae) have been
extensively researched (e.g., Hoffmann et al., 1995; Upadhyay et al., 2001; Knutson,
2005). Trichogramma papilionis has received limited research attention in general,
despite occurring in areas where it might be a valuable natural enemy of some critical
pest species. The first record of T. papilionis from the Hawaiian Islands was reported in
(Oatman et al., 1982). Trichogramma spp., which are egg parasitoids of a variety of
insect pests, especially Lepidoptera, are often mass-reared in large numbers for use in
augmentative biological control.
Ease of mass-rearing is a significant benefit of Trichogramma spp., but may also
result in reductions in insect quality and fitness. There are many issues with captive
rearing of parasitoids that may impact their effectiveness as biological control agents,
including inbreeding, adaptation to captive rearing conditions, and loss of fitness within
2
colonies. The number of individuals used to start captive colonies has the potential to
influence a number of these factors.
The efficient location of hosts is fundamentally essential for parasitoid success in the
field (Wang et al., 2016). Egg parasitoid females have evolved various searching
behavior tactics to find their hosts in nature the cues they use range from visual to
olfactory, or semiochemical, ones. Many species use multiple types of cues, often at
different scales. For example, T. ostriniae has been shown to use visual and olfactory
cues in searching, as well as some degree of random searching (Gardner and Hoffmann,
2020). Inducible plant volatiles and host cues that are induced by the interactions of
herbivorous insects and plants are among the most effective semiochemical compounds
that a female wasp can exploit to discriminate its hosts under complex environmental
conditions. Chemical cues could be a critical point in host selection and searching
behavior in many parasitoid Hymenoptera, including Trichogramma species (Lewis and
Martin, 1990; Schmidt, 1994; Fatouros et al., 2005). Host-specific cues may be very
related to Trichogramma searching behavior and may compete with many other habitat-
related cues (Wright, 2019). Olfactory cues have a crucial role in host-natural enemy
searching behavior in terms of host location and egg- deposition and have been studied
more extensively for parasitoids than predators (Steidle and Van Loon, 2002). Some
plant species have been shown to release secondary-metabolic compounds, often as
volatiles from the leaves or the roots, into their environment as a response to insect
feeding and oviposition (Dicke et al., 2003; Rasmann et al., 2005; Dicke et al., 2009).
Herbivore induced plant volatiles (HIPV) have attracted numerous studies, while few
have been done on oviposition induced plant volatiles (OIPVs) (Schroder et al., 2005).
3
Hilker and Meiners (2006) reviewed the most recent studies on egg-deposition and
inducible plant volatiles that plants may use as defensive strategies against herbivorous
attack. They highlighted mechanisms of the defensive strategy that might be responsible
for the elicitation of plant synomones. These include the interaction between plant cells
and egg-deposition on the plant's surface and the effect of endosymbiotic microorganisms
on both plant tissue and the host insect. Wajnberg and Colazza (2013) highlight elements
of parasitoid behavior and focus on strategies of manipulating the behavior of parasitoids
to maximize the effects of these beneficial insects in pest management.
As part of the natural ecosystem, parasitoids have intimate interactions with other
organisms in their environment. It is crucial to elucidate parasitoid-herbivore-plant
relationships among trophic levels (Ode, 2013). Studying this relationship allows us to
achieve a better understanding of how parasitoid wasps perform. With this, we may be
able to increase the effectiveness of parasitoid wasps against target pests (Meiners and
Peri, 2013). According to Nordlund et al. (1988), host-habitat location in nature, host
location (e.g., host position on the plant), and host acceptance are considered to be the
most critical steps for successful parasitism.
Similarly, Vet and Dicke (1992) distinguished three different searching strategies
used by female wasps: infochemical (semiochemical) trails or plumes from different life
stages of the host, herbivore-induced plant volatiles, and associative learning. Some cues
can be reliable but less easily detected due to their minute quantities in the environment
and may not predictably indicate the host presence, especially over a long distance, this
approach is known as the reliability-detectability theory (Vet and Dicke, 1992). For
example, cues derived from an insect host can be extremely reliable. Still, they may not
4
be as easily detected as plant volatiles because of the huge biomass of plant material
relative to insect hosts (Colazza et al., 2010). Some stimuli are considered to offer
limited information about the host quantitatively but are more reliable because they come
directly from the host eggs, and can be important for generalist species. These stimuli
include egg contact kairomones, egg volatile kairomones, and plant synomones induced
by egg deposition (Colazza et al., 2010). Other stimuli originate from different life stages
of the host or from the plants, where plant stimuli can be more detectable as they are
released in higher quantities. These include cues from scales from adult lepidoptera, adult
traces, host pheromones, and allomones, as well as plant synomones induced by the
feeding activities of immature stages of herbivores, herbivores induced plant volatiles
(HIPVs), but HIPVs may not be as reliable an indicator of the existence of host eggs (Vet
and Dicke, 1992; Fatouros et al., 2008; Colazza et al., 2010).
1.2 Aims of this dissertation: Central hypothesis:
This dissertation study was conducted to address the central hypothesis that
fitness of Trichogramma papilionis under captive mass rearing conditions may be
optimized by avoiding intensive inbreeding, and that T. papilionis depends on chemical
cues in the environment to locate their hosts, and hence understanding of searching
ecology of T. papilionis can be used to improve augmentative biocontrol agents'
performance.
5
1.3 Dissertation organization
This dissertation is divided into six chapters as follows:
1) Chapter one: General introduction and dissertation structure. This
chapter describes the research problem and outlines the importance of egg
parasitoid wasps in augmentative biological control.
2) Chapter two: Effect of founder colony size. The goal of this study was to
test the effect of female founder population size on the fitness of progeny of T.
papilionis (Hymenoptera: Trichogrammatidae) over successive generations
and highlight any change in their biological performance. Three fitness
parameters were considered: fecundity (number of eggs per female),
emergence rate, and sex ratio, as well as the influence of different
environmental conditions (temperature range and humidity) on the fitness of
the wasps.
3) Chapter three: Searching behavior in captivity, chemical collection, and
headspace analysis. Searching behavior of T. papilionis in response to host
eggs, host plants, and induced volatile plant cues was examined using Y- tube
olfactometry. The chapter investigated the ability of T. papilionis females to
respond to egg host cues (Helicoverpa zea and Ephestia kuehniella), and
different plant habitats (sunn hemp and maize) and examined the effect of
oviposition by H. zea on sunn hemp leaves on T. papilionis host searching.
Headspace analysis and thermal desorption and gas chromatography-mass
spectrometry (TD-GCMS) were used to determine the volatile organic
components from sunn hemp Crotalaria juncea (L.) and Helicoverpa zea
6
(Boddie) (Noctuidae) eggs that might influence T. papilionis searching
responses.
4) Chapter Four: Olfactory bioassays. This chapter evaluated the response of
T. papilionis wasps, in Y-tube olfactory bioassays, to blends of synthetic
semiochemicals identified in Chapter 3 as potential attractants. The primary
objective was to identify an optimal combination of compounds that serve as
attractants to T. papilionis.
5) Chapter Five: Semiochemical trials (greenhouse and field conditions).
The effect of synthetic plant-derived semiochemicals on the searching
behavior of T. papilonis in different environments was analyzed. The response
of T. papilionis to a combination of volatiles previously identified in
olfactometer studies was studied under greenhouse and field conditions.
6) Chapter Six: General conclusions and recommendations. This chapter
provides brief concluding comments and recommendations for further studies.
7
References
Chailleux, A., Desneux, N., Seguret, J., Do Thi Khanh, H., Maignet, P., Tabone, E. 2012.
Assessing European egg parasitoids as a means of controlling the invasive South
American tomato pinworm Tuta absoluta. PLoS ONE 7: e48068.
Colazza, S., Peri, E., Salerno, G., Conti, E. 2010. Host searching by egg parasitoids:
exploitation of host chemical cues. In: Parra, J.R.P., Consoli, F.L., Zucchi, R.A.
editors. Egg parasitoids in agroecosystems with emphasis on Trichogramma.
Springer. 97-147.
Dicke, M., Van Loon, J.J., Soler, R. 2009. Chemical complexity of volatiles from plants
induced by multiple attack. Nature Chemical Biology 5: 317–24.
Dicke. M, van Poecke, R.M.P., De Boer, J.G. 2003. Inducible indirect defense of plants:
from mechanisms to ecological functions. Basic and Applied Ecology 4: 27-42.
Fatouros, N.E., Bukovinszkine’Kiss, G., Kalkers, L.A., Soler Gamborena, R., Dicke, M.
& Hiker, M. 2005. Oviposition-induced plant cues: Do they arrest Trichogramma
wasps during host location? Entomologia Experimentalis et Applicata 115: 207-
215.
Fatouros, N.E., Dicke, M., Mumm, R., Meiners, T., Hilker, M. 2008. Foraging behavior
of egg parasitoids exploiting chemical information. Behavioral Ecology 19: 677-
689.
Gardner, J., Hoffmann, M.P. 2020. How important is vision in short-rage host finding by
Trichogramma ostriniae used for augmentative biological control? Biocontrol
Science and Technology https://doi.org/10.1080/09583157.2020.1743816
8
Hilker, M., Meiners, T. 2006. Early Herbivore Alert: Insect Eggs Induce Plant Defense.
Journal of Chemical Ecology 32: 1379-1397. DOI:10.1007/s10886-006-9057-4.
Hoffmann, M.P., Walker, D.L., Shelton, A.M. 1995. Biology of Trichogramma ostriniae
(Hymenoptera: Trichogrammatidae) reared on Ostriniae nubilalis (Lepidoptera:
Pyralidae) and survey for additional hosts. Entomophaga. 40: 387-402.
Knutson, A. 2005. The Trichogramma Manual: A guide to the use of Trichogramma for
biological control with special reference to augmentative releases for control of
bollworm and budworm in cotton. Texas Agricultural Extension Service # B-
6071, 42 pp.
Lewis, W.J., Martin, W.R.J. 1990. Semiochemicals for use with parasitoids: status and
future. Journal of Chemical Ecology 16: 3067-3089.
Mansour, M. 2010. Effects of gamma radiation on the Mediterranean flour moth,
Ephestia kuehniella, eggs and acceptability of irradiated eggs by Trichogramma
cacoeciae females. Journal of Pest Science 83: 243-249.
Meiners, T., Peri, E. 2013 Chemical ecology of insect parasitoids: essential elements for
developing effective biological control programmes. In: Wajnberg E, Colazza S
(eds) Chemical ecology of insect parasitoids. Wiley-Blackwell, UK, pp 193-224.
Nordlund, D.A., Lewis, W.J., Altieri, M.A. 1988. Influences of plant-induced
allelochemicals on the host/prey selection behavior of entomophagous insects.
Novel Aspects of Insect–Plant Interactions (ed. by P. Barbosa and D.K.
Letournneau), pp. 65-90. Wiley, New York.
Oatman, E.R. Pinto, J.D., Platner, G.R. 1982. Trichogramma (Hymenoptera:
Trichogrammatidae) of Hawaii. Pacific Insects 24: 1-24.
9
Ode, P. J. 2013. Plant defenses and parasitoid chemical ecology. in Chemical Ecology of
Insect Parasitoids, eds E. Wajnberg and S. Colazza (Oxford: Wiley-Blackwell),
11–28.
Rasmann, S., Kçllner, T.G., Degenhardt, J., Hiltpold,I., Toepfer, S., Kuhl-mann, U.,
Gershenzon, J., Turlings, T.C.J. 2005. Recruitment of entomopathogenic
nematodes by insect-damaged maize roots. Nature 434: 732-737.
Schmidt, J.M. 1994. Host recognition and acceptance by Trichogramma. Biological
control with egg parasitoids (ed. by E. Wajnberg and S. Hassan) pp. 165-200.
CAB International, Wallingford, Oxon, UK.
Schroder, R., Forstreuter, M., Hilker, M. 2005. A plant notices insect egg deposition and
changes its rate of photosynthesis. Plant Physiology 138: 470-477
Smith, S.M., 1996. Biological control with Trichogramma: advances, successes, and
potential of their use. Annual Review of Entomology 41: 375-406.
Steidle, J.L.M., Van Loon, J.J.A. 2002. Chemoecology of parasitoid and predator
oviposition behaviour, pp. 291-318, in Hilker, M. and Meiners, T. (eds.).
Chemoecology of Insect Eggs and Egg Deposition. Blackwell, Berlin.
Suckling, D.M., Brockerhoff, E.G. 2010. Invasion biology, ecology, and management of
the light Brown apple moth (Tortricidae). Annual Review of Entomology 55: 285-
306.
Upadhyay, R.K., Mukerji, K.G., Chamola, B.P. 2001.Biocontrol potential and its
Exploitation in Sustainable Agriculture: Insect Pests. Kluwer Academic/ Plenum
Publishers. Pages?
10
Vet, L.E.M., Dicke, M. 1992. Ecology of infochemical use by natural enemies in a
tritrophic context. Annual Review of Entomology 37: 141-172.
Wajnberg, E., Colazza, S. 2013. Chemical Ecology of Insect Parasitoids. Wiley-
Blackwell, pp. 328. SBN: 978-1-118-40952-7.
Wang, D., Lu, L., He, Y., Shi, Q., Wang, G. 2016. Effects of insecticides on oviposition
and host discrimination behavior in Trichogramma chilonis (Hymenoptera:
Trichogrammatidae). Journal of Economic Entomology 109: 2380-2387.
Wright, M.G. 2019. Cover crops and conservation biocontrol: can the impacts of
Trichogramma (Hymenoptera: Trichogrammatidae) be magnified? Annals of the
Entomological Society of America 112: 295-297.
11
CHAPTER 2
FITNESS EFFECTS OF FOUNDER FEMALE NUMBER OF TRICHOGRAMMA
PAPILIONIS REARED ON A FACTITIOUS HOST EPHESTIA KUEHNIELLA
(ZELLER).
Abstract
Trichogramma species (Hymenoptera: Trichogrammatidae) are egg parasitoids of
a variety of insect pests, especially Lepidoptera. Trichogramma are often mass-reared
in large numbers for use in augmentative biological control. There are many issues
with captive rearing of parasitoids that may impact their effectiveness as biological
control agents, including inbreeding and loss of fitness within colonies. The goal of
this study was to test the effect of female founder population size on the fitness of
progeny of T. papilionis over successive generations and highlight any change in
their biological performance. Two parasitoid lines were started from 1, 2, and 10
inseminated founder females from wasps that were initially collected from Lampides
boeticus L. (Lycaenidea) eggs in sunn hemp Crotalaria juncea fields. The progeny of
these founder females was tracked for ten generations, to evaluate their fitness and
performance. Fitness parameters were considered: fecundity (number of eggs per
female), emergence rate, and sex ratio, as well as the influence of different
environmental conditions (temperature range and humidity) on the fitness of the
wasps. The results showed no significant difference for eggs laid per female over ten
generations, suggesting that the imposed bottleneck did not result in reduced female
fecundity for any founder population size. However, low founder numbers did affect
both the emergence rate and sex ratio of T. papilionis. These results suggest that
establishing a new colony of wasps with at least moderate founder numbers is better
to avoid any significant loss in quality of biological characteristics as long as rearing
is done under appropriate conditions (25 ± 2◦C, 60 –70% RH, LD 16: 8 h).
Keywords: Trichogramma papilionis, Factitious host, Ephestia kuehniella, Founder
female, Population fitness.
12
2.1 Introduction
Several species of egg parasitoids are commonly used in biological control
programs, and can potentially play a valuable role in suppressing pests through
decreasing the number of emerging larvae (Van Driesche and Bellows, 1996; van
Lenetern, 2003). Trichogramma spp. (Hymenoptera: Trichogrammatidae) are among the
most widely applied and studied augmentative biological control agents. These parasitoid
wasps are used in biological control programs against a diversity of phytophagous pests
in many economically important crops (Hassan, 1993; Wajnberg and Hassan, 1994;
Smith, 1996; Parra and Zucchi, 2004), in part because they can be inexpensively reared
on factitious hosts (Li, 1994; Smith, 1996; Parra, 1997; Haji et al., 1998; van Lenteren,
2003; Parra and Zucchi, 2004). Trichogramma wasps primarily parasitized the eggs of
Lepidoptera species (moth and butterflies). Some Trichogramma species can also attack
hosts in a broad range of habitats and parasitized the eggs of different insects such as
lacewings, flies, true bugs, beetles, other wasps (Knutson, 1998). Trichogramma species
were mass-produced initially in the early 1900s after entomologists discovered the
potential successes of using them in biological control programs, despite the few
commercial attempts to produce these wasps in the U.S. (Knutson, 1998).
Trichogramma are mostly reared in laboratory circumstances on a factitious host
such as Mediterranean flour moth Ephestia kuehniella (Zeller) (Lepidoptera: Pyralidae)
(Parra, 1997; Bertin et al., 2017), which is not the intended target host of the wasps
(Bertin et al., 2017). Factitious hosts are used as they are typically less costly, and high
quality of mass-reared parasitoids can be achieved, even though rearing the egg
parasitoids in a factitious host may result in an evolutionary interaction over successive
generations, selecting for a captive condition strain of the wasps (Hoffmann et al., 2001).
13
After mass-rearing, the egg parasitoids are ready to be liberated as biocontrol agents,
usually in crop fields under varied environmental conditions. There are however
drawbacks associated with mass-rearing insect in captivity, that may lead to a decrease in
the quality of insects produced (Bertin et al., 2017) and most of these potential problems
are related to the genetic diversity of the colonies, inbreeding depression, accumulation of
detrimental mutations, and genetic adaptation to captive conditions (Frankham et al.,
2002). Many desirable aspects in egg parasitoids (e.g., physiological, phenotypic, and
behavioral characteristics) may vary in vitro when the parasitoids are reared on
alternative hosts, and that may result in undesirable changes in the performance of the
parasitoids under field environments (Leppla and Fisher, 1989; Hopper et al., 1993).
Genetic drift, an evolutionary process in which the frequency of an existing gene variant
(allele) in a population changes over a period of time or generations in small populations
is considered a primary cause of the loss of genetic diversity of species (Joslyn, 1984;
Allendorf, 1986; Hopper et al., 1993; Gabriel et al., 1991; Gabriel and Bürger, 1994;
Oostermeijer et al., 2003; Frankham, 2005; Grueber et al., 2013).
Genetic drift has the most significant negative impact on small populations
(Prezotti et al., 2004), which should be taken under consideration when establishing
laboratory colonies of insects, to ensure that an adequate number of individuals are used
to create the colony, and in the long-term, to sustain a genetically viable captive
population (Wajnberg, 1991). There are, however, no generally agreed-upon rules about
the ideal number of individuals required to create a new viable population in vitro, which
may be started from less than ten individuals, to hundreds or even thousands of
individuals (Mackauer, 1976; Bartlett, 1985). Many researchers have shown or suggested
14
that rearing egg parasitoids on alternative hosts over many generations can cause the
parasitoids to deviate either in host preference, or ability to effectively locate and
parasitize target hosts under field conditions. Ultimately this might lead to adverse
impacts on parasitoid fitness and declining field performance with continued captive
rearing (Kaiser et al., 1989; van Bergeijk et al., 1989; Hassan and Guo, 1991; Woodworth
et al., 2002; Antolin et al., 2006; Araki et al., 2007; Henry et al., 2008; Li et al., 2010).
Accumulation of deleterious recessive alleles is also more likely in captive colonies,
probably more so in those started from very few founders (Bartlett, 1984; Stephens et al.,
1999). A population comprises a set of variable genotypes compounded by the number of
different individuals (Luque et al., 2016). Population size is considered one of the
determinants of genetic structure (Nielsen and Slatkin, 2013). Founder number may thus
affect newly established colonies by demographic and genetic mechanisms such as
recessive allele expression, and demographic stochasticity (Lande, 1993; Boyce et al.,
2006).
Genetic mechanisms have received intense attention in terms of inbreeding
depression, which can significantly increase the short-term potential for extinction during
the process of colonization of a habitat (Newman and Pilson, 1997; Bijlsma et al., 2000;
Reed et al., 2002, 2003). Individual founders that have heterogenic genes and phenotypic
variation are more likely to be successful colonizers (Drake, 2006; Wagner et al., 2017;
Forsman, 2014; Szűcs et al., 2017). When establishing new populations of bio-control
agents, researchers typically seek to maximize the fitness of the individuals by avoiding
the adverse impacts of inbreeding for the founder and early generations in captivity
(Castañé et al., 2014). Genetic heterogeneity of colony founders has an effect on the
15
potential for inbreeding depression, and the number of individuals that are used to
establish a new colony significantly affect the heterogeneity. It may be a simple matter
for some species, for researchers to find an adequately large number of individuals to
establish a new colony, while for other species, this may be a limiting factor (Castañé et
al., 2014). Regardless of the genetic mechanisms, the number of founders is persistently
identified as a fundamental determinant of colonization success across a diverse range of
taxa (Lockwood et al., 2005; Colautti et al., 2006; Blackburn et al., 2015).
In seeking to identify species that may have potential for positive impacts in
augmentative and conservation biocontrol programs in Hawaii, Trichogramma papilionis
was identified as a species that may possess valuable characteristics. Trichogramma
papilionis has received limited research attention in general. The first record of T.
papilionis from the Hawaiian Islands was reported in Oatman et al., (1982). It is readily
reared in captivity on factitious hosts (Wright unpublished data).
This study aimed to test the effect of the initial number of founder females on life-
history characteristics and leading fitness-proxies of resulting populations, including
fecundity of females, adult emergence rate, sex ratio, mean parasitized eggs per female.
16
2.2 Materials and Methods
2.2.1 Egg parasitoid colony
A T. papilionis colony was established from Lampides boeticus L. (Lycaenidae)
eggs collected on sunn hemp plants, Crotalaria juncea, Waialua, O’ahu Island, Hawaii,
USA. The wasps were maintained on E. kuehniella eggs in a climate-controlled room (25
± 1◦C, 50–70% RH, LD 16: 8 h) (Huigens et al., 2009, 2010) for multiple generations
over fifteen months, until the experiment started in the laboratory. E. kuehniella eggs
parasitized by T. papilionis were held in Plexiglas cages (15x15x15cm) under the
environmental conditions mentioned above. Upon emergence, adult parasitoids were
provided clusters of Ephestia eggs glued to the surface of a sheet of paper using “Elmer’s
glue-all®”, with droplets of pure honey as an energy source. Wasps of both genders lived
for 8-10 days when they were provided with honey droplets. T. papilionis females used in
experiments were 24 h old and were left to mate with males during that period. Males
emerged about 12 h before females and waited on other parasitized eggs for female
emergence. Copulation occurs immediately after female emergence. All experiments
were conducted in the laboratory.
2.2.2 Experimental populations
2.2.2.1 Evaluation of the effects of the number of founder females
To test the effects of the number of founder females upon starting a new colony in
the laboratory, three different founder population sizes (1, 2 and 10 mated female wasps)
were used: 1, 2 and 10 gravid females were isolated from the original colony into small
17
glass vials (4.5 cm length, 0.5 cm diameter), these vials were closed with perforated
screened lids for ventilation. The glass vials and their covers were reused for repeated
generations after being washed with detergent liquid and tap water then autoclaved at
121°C at 100 kPa for 15 minutes. Ten replicates were used for each founder population
size - each vial equaled one replicate. The vials were placed in a tube rack. A droplet of
pure honey was placed into each vial with a small needle, which was connected to a 5-cc
syringe to feed the wasps throughout the experiment.
2.2.2.2 Establishing isofemales and other lines.
To establish lines from generations produced from the original founders, the
females were placed individually into glass vials and offered clusters of E. kuehniella
eggs for parasitism. These clusters of E. kuehniella eggs were glued on small strips of
yellow paper using “Elmer’s glue-all®”. The strips of factitious host eggs were UV
irradiated for 30 min. before being introduced into the glass tube, to reduce the likelihood
of fungal contamination (Stein and Parra, 1987). Ephestia egg patches were observed
from being parasitized after exposure to female wasps until adult emergence. Four trails
were created.
To estimate the effects of different environmental conditions on the colonies,
combined with the sizes of the founder-female number of wasps, two experimental lines
were established. One line was kept in a climate room for insect rearing (25 ± 2◦C, 60 –
70% RH, LD 16: 8 h), which represented the “Mass-rearing room line” (M) and another
line was kept in a laboratory with different ambient conditions (22 ± 1◦C, 75-88% RH,
LD 16:8h), the so-called “Laboratory line” (L).
18
After the adult wasps emerged from each generation, the population lines were
continued, through allowing females to mate with males from the same replicate for 24-
48 h, after which individual females were randomly chosen and isolated + in new glass
tubes that contained droplets of pure honey as a nutrient and energy source (Bertin et al.,
2017). The same number of the founder females (1, 2 and 10 female wasps) were isolated
from each respective founder colony used to create the original replicate populations
(subpopulations). Thus, one mated female was taken from the one-female founder
colony, two mated females from the two founder-female colony, and ten mated females
were taken from the ten-founder colony. These females were then placed gently into the
glass tubes as described above. Females were distinguished from the males based on the
sexual dimorphism in the antennae (Bowen and Stern, 1966). Antennal dimorphism was
used to identify sexes, using the antennomere number, which is higher in males, as well
as males have different antennae shape, filiform and rarely forming an apical club,
whereas, in females, the last flagellomeres are enlarged and swollen, (Romani et al.,
2010). A dissecting microscope was used to visually confirm the sex of the wasps.
2.2.2.3 Evaluating fitness-proxies of the founder females over successive generations
Three parameters were used for measuring the fitness for each founder population
over 10 generations: fecundity (the number of parasitized eggs per female), emergence
rate of progeny, and sex ratio of progeny. These fitness parameters were traced for the
founder treatments from the initial founder females through the tenth generation. To
quantify the number of eggs laid per female after each parasitism period, the numbers of
19
parasitized eggs in each vial were separately counted aided by a laboratory counter
(Fisher Scientific), using the dissecting microscope. The number of blackened eggs,
which denoted that the egg was parasitized and that the parasitoid larvae are developing,
was used to distinguish parasitized eggs from unparasitized ones. The percentage rate of
subsequent emergence of adult wasps was estimated by counting the emergence holes on
parasitized eggs, divided by the total number of darkened parasitized eggs (with and
without emergence holes) (Pratissoli et al., 2005). The sex ratio of adult wasps was
quantified as the number of males and females emerging from eggs in each vial for each
generation. Parasitized eggs per female was estimated by dividing the total number of
parasitized eggs of Ephestia per vial by the number of founder females (Bowen and
Stern, 1966; Bertin et al., 2017).
This experimental design aims to test the following hypothesis: rearing
Trichogramma wasps in a factitious host with variable numbers of founders (1, 2 and 10
mated females), and under a variety of rearing conditions will result in inbreeding
depression and might result in a subsequent reduction in fitness of the progeny.
2.2.3 Statistical analyses
Analysis of variance (ANOVA) was conducted using JMP13 Pro (SAS Institute,
Carey, NC). Female fecundity (production of eggs, and percentage of eggs per female),
the emergence of adults, and sex ratio were fitted to a mixed linear model with treatment
and generations as fixed factors, replicates as random factors, and overlapping
generations. Least square means differences Tukey (HSD) were used to compare means
20
for parasitized eggs per female, sex ratio, emergence rate, and generations among
treatments. The full data set was used to estimate p-values for founder-size effects (Szűcs
et al., 2017). Comparisons of sex ratio and parasitized eggs per female versus lines and
those of the 10th generation were analyzed by a Student’s t-test (Castañé et al., 2014).
2.3 Results
2.3.1 Fitness measures of Trichogramma papilionis
The outcomes of this experiment revealed significant differences for both
emergence rate and sex ratio among the three founder-population sizes for T. papilionis
(F(4,639) = 25.3, p < 0.0001 and F(4,639) = 27.1, p < 0.0001) respectively, whereas, no
significant difference for number of eggs laid per female was found among treatments.
There were substantial significant differences between the breeding cohorts in the
laboratory colony and the mass-rearing room colony, in terms of sex ratio and parasitized
eggs per female (F (4,639) = 5.93, p < 0.015 and F (4,639) = 8.18, p < 0.0044 respectively
(Table 1).
21
Table 1: Analysis of variance of Trichogramma papilionis fitness parameters as affected
by founder population and environmental conditions (25°C vs 22°C) over 10 successive
generations in captivity. Laboratory line: 22 ± 2 ºC, 60 –70% RH, LD 16:8 h. photoperiod.
Mass-rearing line: 25 ± 1ºC, 75-88% RH, LD 16:8 h. photoperiod. * Indicates a significant
effect, P < 0.050, LSD test.
Fitness
Parameters Statistical
Parameter Estimate Stander Error
(SEM) F value p value
Emergence
rate
Intercept 92.4 0.85 108.20 0.0001
Experiment 0.67 0.85 0.59 0.44
Treatments 2.67 1.19 25.56 0.0001 *
Lines -1.5 0.85 3.16 0.075
Sex ratio
Intercept 81.1 0.77 104.15 0.0001*
Experiment 0.5 0.77 0.41 0.51
Treatments 1.54 1.08 27.2 0.0001 *
Lines -1.9 0.77 5.93 0.015 *
Parasitized
eggs
per female
Intercept 32.8 0.6 49.77 0.0001
Experiment 1.1 0.6 3.0 0.083
Treatments 0.8 0.92 1.30 0.272
Lines -1.8 0.65 8.18 0.0044*
22
2.3.2 Emergence rate response
The results show that there are statistical differences in the mean emergence rate
among the female founder colony sizes. There was no significant difference in emergence
rate of progeny between ten and two founder females. However, ten and two female
founders have a significantly higher progeny emergence rate compared to one female
founder colonies (Figure 1). Emergence rates had different patterns among treatments
over generations. Founder populations of ten and two females showed consistent patterns
of adult emergence over multiple generations, whereas founder populations with just one
female had substantial variation among generations, and 2 founders was intermediate,
with 10 founders most consistent (Figure 2). No significant difference in the emergence
rate between the two experimental lines (M and L) was detected (data not shown).
Figure 1: Response (Mean ± SEM) in the emergence rate of three founder
population sizes (1, 2, and 10 founder females) of Trichogramma papilionis over ten
serially bottlenecked generations. Treatments not connected by the same letter were
significantly different
One Two Ten0
20
40
60
80
100
% E
mer
genc
e ra
te
aab
No. of founder females
23
Figure 2: Coefficient of variation in the emergence rate of Trichogramma papilionis
from three founder population sizes (Treatments, 1, 2, 10 females) over ten generations.
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
1 Female
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
2 Females
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
10 Females
24
2.3.3 The response of sex ratio
Overall, the sex ratio of the offspring was generally female- biased among
treatments, with significant differences among all treatments (Figure 3). Ten founder
females consistently produced a greater ratio of females than two- and one founders.
There was a significant difference in sex ratio between the two experimental lines (L and
M), where the mass rearing room (M) line produced significantly, albeit slightly, more
females (83.0 ± 1.1%) than the lab line (L) (79.2 ± 1.1%) (Figure 4; t = 2.32; d.f. = 631; p
= 0.010).
Figure 3: Trichogramma papilionis sex ratios of progeny from three founder female
treatments (1, 2, and 10 founder females). Values are estimated mean (± SEM). Bars not
connected by the same letter are significantly different.
One Two Ten 0
20
40
60
80
100
ab c
No. of founder females
Sex
ratio
(% fe
mal
e)
25
Figure 4: Mean estimates (± SEM) of the sex ratio of Trichogramma papilionis in two
experimental lines (22°C, L-line, and 25°C, M-line). Treatments not connected by the
same letter were significantly different.
2.3.4 Parasitized eggs per female
There were no statistically significant differences among treatments for
parasitized eggs per female (Figure 5). Additionally, founder population sizes of ten and
two females showed less variation over the 10 generations than the one founder-female
colonies, with the single female colonies showing consistent high variability in fecundity
(Figure 6). The results showed a small difference between the two experimental lines (L
and M), with significantly higher (t = 2.79; d.f. = 631; p = 0.0027), numbers of
parasitized eggs in the warmer mass rearing room (34.7 ± 0.92 eggs per female)
compared to the 3°C cooler laboratory-reared line (30.98 ± 0.94).
22°C 25°C76
78
80
82
84
86
a
bSe
x ra
tio (%
fem
ale)
26
Figure 5: Mean (± SEM) number of Ephestia eggs parasitized per Trichogramma
papilionis female for the three founder treatments (1, 2 and 10 founder females). Bars not
connected by the same letter are significantly different.
One Two Ten0
10
20
30
40
Mea
n nu
mbe
r of e
ggs
laid
pe
r fem
ale
aaa
No. of founder females
27
Figure 6: Coefficient of variation in percentage parasitized Ephestia eggs for three
different founder population size colonies (Treatments, 1, 2, and 10 founder females) of
Trichogramma papilionis over 10 successive generations
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
1 Female
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
2 Females
0 2 4 6 8 100
20
40
60
80
Generation
CV
%
10 Females
28
2.4 Discussion
2.4.1 Variability among the fitness parameters
Overall, there was considerable variation in the essential characteristics of
parasitoid fitness across generations as a result of different founder population sizes.
There were significant differences in sex ratio and adult wasp emergence rate among
three different founder population sizes of T. papilionis, with the smallest, single female
founder populations showing the lowest fitness. Additionally, the wasps exhibited
different performances within two different environmental conditions in terms of their
fecundity, the mean number of parasitized host eggs per female. These results strongly
suggest that the number of founder females impacts multiple aspects of the progeny
fitness over generations, reducing fitness with female isolines, but remaining surprisingly
fit in colonies initiated even with only two females.
This study showed that there was no significant difference in the mean number of eggs
laid per female across generations irrespective of founder number. The level of eggs laid
per female was more consistent in the ten and two founder-female treatments than the
single-founder treatment, which suggests that increasing founder size has benefits in
terms of consistency of productivity in the wasps over multiple generations. Using a
factitious host with a low number of founder females might be responsible for
undesirable consequence when establishing a new colony of parasitoids. Hoffmann et al.
(2001) showed that T. ostriniae, a parasitoid of Ostrinia spp. (Pyralidae), reared on E.
kuhniella had typical longevity, but had lower fecundity compared with wasps that were
raised in different hosts, such as Ostrinia nubilalis and Citotroga cerealella. Moreover,
they suggested that wasps emerging from the inferior-quality hosts performed poorly
29
even when offered a higher-quality host, implying that Ephestia eggs produced lower
quality wasps, possibly with epigenetic effects that produce multiple reduced-quality
generations. A study by Prezotti et al. (2004) compared the effect of three founder sizes
on the quality of sexual populations of Trichogramma pretiosum under controlled
conditions. Their results indicated that the fecundity (mean number of eggs parasitized)
of progeny of one, five, and ten pairs of T. pretiosum varied significantly, where a
negative regression was observed between the mean number of laid eggs per female and
the inbreeding coefficient. Single-pair colonies showed a 14% reduction in the rate of
parasitism compared to the 10-pair colony. The results of this present study contrast with
the findings of Prezotti et al. (2004), where there was no significant difference in the
mean number of laid eggs per female for 1, 2, and 10 founder females. In addition, all
other studied traits (emergence rate, sex ratio, longevity, and percentage of deformed
adults), in the Prezotti et al. (2004) study, were not significantly different among all
parental population sizes. The results of the current study also have some similarities to
Prezotti et al. (2004), in how the performance of founder size significantly varied over
generations, with lower numbers of parental insects producing progeny that had more
variable performance. Trichogrammatidae in general, are considered to be arrhenotokous
(Hamilton, 1967; Stouthamer and Kazmer, 1994; Russell and Sothermare, 2011),
resulting in extreme female-biased sex ratios (Suzuki and Hiehata, 1985). The sex ratio of
T. papilionis was significantly affected by the initial number of founder females in the
colony, albeit possibly because some of these females were not inseminated prior to
removal from the emergence sites, where the high sex ratios of female wasps are closely
related to fertilization rate (Suzuki and Hiehata,1985).
30
Furthermore, the influence of various rearing conditions on the biological
characteristics of T. papilionis progeny was considered. In this study, founder wasps
showed varied performance in terms of reproduction and sex ratio of progeny when
reared under different environmental conditions. Similarly, Pratissoli et al. (2005)
showed that the sex ratio of T. pretiosum and T. acacioi progeny was affected by
temperature, while the number of individual wasps per parasitized egg was not affected.
The emergence rate (viability) of the progeny varied among treatments in the
experiments reported here. Ten and two founder wasps showed a higher level of viability
over multiple generations; single-founder colonies had an inconsistent pattern in
emergence rate across generations. Pratissoli et al. (2005) found that there was an effect
of varying temperatures on the emergence (eclosion) rate of T. pretiosum and T. acacioi
adults where they found a higher emergence rate for both species at 20, 25 and 30 ºC,
which is not consistent with the results presented here, where the emergence rate was
similar in both lines. Inbreeding between closely related individuals may result in
expression of recessive traits, due to the similarity between the pair mates’ genomes.
Inbreeding issues are known to have negative effects on fitness traits (Frankham, 2005).
inbred individuals are more likely to be sensitive to environmental stress than outbred
individuals, perhaps because environmental stress promotes the expression of detrimental
recessive alleles (Fox et al., 2011). However, this is not always the case, some studies
showed a significant correlation between inbreeding depression and extreme
environments, while other studies have shown the opposite (Fox et al., 2011; Frank and
Fischer, 2013). When Frank and Fischer (2013) studied the effect of the three
temperature treatments and the interaction with inbreeding in the tropical butterfly
31
Bicyclus anynana they found that in spite of even low inbreeding level, temperature
significantly affected some fitness-related traits including fecundity and egg hatching
success. However, they concluded that the results of their study did not support the
hypothesis that sensitivity to environmental stress is more likely to occur in inbred
individuals than outbred ones, despite the significant effect of temperature treatment on
some fitness measures. Fox et al., (2011) found good evidence for the effect of varying
temperatures on the larval development of the seed-feeding beetle, Callosobruchus
maculatus; rearing at 20°C did not impose significant stress on the outbred beetles, yet it
did impose the most stressful environment for inbred larvae. Here in the present study,
two different rearing temperatures showed varied effects on some fitness-related traits.
Sex ratio and female fecundity of T. papilionis progeny over multiple generations were
more impacted at the lowest rearing temperature. I suspect that the effects of inbreeding
depression become more evident at the lower, and possibly more stressful rearing
temperatures tested, as showed by Fox et al., (2011).
In conclusion, it is clear that larger numbers of founder insects are likely to
produce higher quality colonies in the long term. My data showed that as few as two
founder females provided acceptable emergence rate of wasp progeny, despite some
increased variability overall. A single founder female produced poor colonies as
measured by most fitness proxies measured. Interestingly, the three different founder size
treatments almost had the same parasitism rate. Rearing conditions impacted the
performance of the wasps. Additional work is needed to determine why more female
progeny and eggs per female were produced under the slightly warmer rearing
conditions.
32
References
Allendorf, F.W.1986. Genetic drift and the loss of alleles versus heterozygosity. Zoo
Biology 5:181-190.
Antolin, M.F., Bjorksten, T.A., Vaughn, T.T. 2006. Host‐related fitness trade‐offs in a
presumed generalist parasitoid, Diaeretiella rapae (Hymenoptera: Aphidiidae).
Ecological Entomology 31:242-254.
Bartlett, A.C.1985. Guidelines for genetic diversity in laboratory colony establishment
and maintenance. In: Singh, P., Moore, R.F. (Eds.), Handbook of Insect Rearing,
Vol. 1. Elsevier, Amsterdam, pp. 7-17.
Bertin, A., Pavinato, V.A.C., Parra, J.R.P. 2017. Fitness-related changes in laboratory
populations of the egg parasitoid Trichogramma galloi and the implications of
rearing on factitious hosts. Biological Control 62: 435-444
Bijlsma, R., Bundgaard, J. & Boerema, A.C. 2000. Does inbreeding affect the extinction
risk of small populations? Predictions from Drosophila. Journal of Evolutionary
Biology 13: 502-514.
Blackburn, T.M., Lockwood, J.L., Cassey, P. 2015. The influence of numbers on
invasion success. Molecular Ecology 24: 1942-1953.
Castañé, C., BuenoVand, H.P., Carvalho, L.M. 2014. Effects of founder population size
on the performance of Orius laevigatus (Hemiptera: Anthocoridae) colonies.
Biological Control 69:107-112.
33
Colautti, R.I., Grigorovich, I.A., MacIsaac, H.J. 2006. Propagule pressure: a null model
for biological invasions. Biological Invasions 8: 1023-1037.
Cônsoli, F. L.; Parra, J. R. P. 1991. Biology of Trichogramma galloi at constant and
fluctuating temperatures. Paper presented at 12th International Plant Protection
Congress, Rio de Janeiro, Rio de Janeiro.
Drake, J.M. 2006. Heterosis, the catapult effect and establishment success of a colonizing
bird. Biology Letters 2: 304-307.
Fox, C.W., Stillwell, R.C., Wallin, W.G., Curtis, C.L., Reed, D.H. 2011. Inbreeding-
environment interactions for fitness: complex relationships between inbreeding
depression and temperature stress in a seed-feeding beetle. Evolutionary Ecology
25: 25–43.
Forsman, A. 2014. Effects of genotypic and phenotypic variation on establishment are
important for conservation, invasion, and infection biology. Proceedings of the
National Academy of Sciences of the USA 111: 302-307.
Frankham, R. 2005. Genetics and extinction. Biological Conservation. 126: 131-140.
Frankham, R., Ballou, J.D., Briscoe, D. A. 2002. Introduction to conservation genetics.
Cambridge University Press, Cambridge.
Franke, K., Fischer, K. 2013. Effects of inbreeding and temperature stress on life history
and immune function in a butterfly. Journal of Evolutionary Biology 26: 517-528.
34
Gabriel, W., Bürger, R. 1994. Extinction risk by mutational meltdown: synergistic effects
between population regulation and genetic drift. Pages 69-84 in Loeschcke, J. V.,
Tomiuk, S. K. Jain, editors. Conservation genetics. Birkhäuser, Basel,
Switzerland.
Gabriel, W., R. Bürger, and M. Lynch. 1991. Population extinction by mutational load
and demographic stochasticity. Pages 49-59 in Seitz, A., Loeschcke, V. editors.
Species conservation: a population-biological approach. Birkhäuser, Basel,
Switzerland. pp 282. DOI https://doi.org/10.1007/978-3-0348-6426-8.
Grueber, C.E., G.P. Wallis, I., Jamieson, G. 2013. Genetic drift outweighs natural
selection at toll-like receptor (TLR) immunity loci in a re-introduced population
of a threatened species. Molecular Ecology. 22: 4470-4482.
Haji, F.N.D., Velasquez, J., Bleicher, E., Alencar, J.A. de, Haji, A.T., Diniz, R.S.1998.
Tecnologia de produção massal de Trichogramma spp. Petrolina, Embrapa-
CPATSA, 24 p.
Hassan, S.A., Guo, M.F. 1991. Selection of effective strains of egg parasites of the genus
Trichogramma (Hymenoptera. Trichogrammatidae) to control the European corn
borer Ostrinia nubilalis Hb. (Lep., Pyralidae). Journal of Applied Entomology
111: 335-341.
Hassan, SA. 1993. The mass rearing and utilization of Trichogramma to control
lepidopterous pests: achievements and outlook. Pesticide Science 37:387-391.
35
Henry, L.M., Roitberg, B.D., Gillespie, D.R. 2008. Host-range evolution in Aphidius
parasitoids: fidelity, virulence and fitness trade-offs on an ancestral host.
Evolution. 62: 689–699.
Hoffmann, M.P., Ode, P.R., Walker, D.L., Gardner, J., van Nouhuys, S., Shelton, A.M.
2001. Performance of Trichogramma ostriniae (Hymenoptera:
Trichogrammatidae) reared on factitious hosts, including the target host, Ostrinia
nubilalis (Lepidoptera: Crambidae). Biological Control 21: 1-10.
Hopper, K.R., Roush, R.T., Powell, W. 1993. Management of genetics of biological
control introductions. Annual Review of Entomology. 38: 27-51.
Huigens, M.E., Pashalidou, F.G., Qian, M.H., Bukovinszky, T., Smid, H.M., van Loon,
J.J.A. et al. 2009. Hitch-hiking parasitic wasp learns to exploit butterfly anti-
aphrodisiac. Proceedings of the National Academy of Sciences of the USA 106:
820-825.
Huigens, M.E., Woelke, J.B., Pashalidou, F.G., Bukovinszky, T., Smid, H.M., Fatouros,
N.E. 2010. Chemical espionage on species-specific butterfly anti-aphrodisiacs by
hitchhiking Trichogramma wasps. Behavioral Ecology 21: 470-478.
Kaiser, L., Pham-Delegue, M.H., Masson, C. 1989. Behavioural study of plasticity in
host preferences of Trichogramma maidis (Hymenoptera: Trichogrammatidae).
Physiological Entomology. 14:53-60.
Mackauer, M. 1976. Genetic Problems in the Production of Biological Control Agents.
Annual Review of Entomology. 21: 396-85.
36
Newman, D., Pilson, D. 1997. Increased probability of extinction due to decreased
genetic effective population size: experimental populations of Clarkia pulchella.
Evolution. 51: 354-362.
Knutson, A. 1998. The Trichogramma manual; A guide to the use of Trichogramma for
biological control with special reference to augmentative releases for control of
bollworm and budworm in cotton. College Station, Texas: Texas Agricultural
Extension Service, Texas A & M University System B-6071.
http://www.soilcropandmore.info/crops/CottonInformation/Production/b-
6071.html
Leppla, N.C., Fisher, W.R. 1989. Total quality control in insect mass production for
insect pest management. Journal of Applied Entomology 108: 452-461.
Li, L. 1994. Worldwide use of Trichogramma for biological control on different crops: A
survey. In: Wajnberg E., Hassan S.A. (eds) Biological control with egg
parasitoids. Cab International, Wallingford, pp 37-51.
Li, L., Wei, W., Liu, Z., Sun, J. 2010. Host adaptation of a gregarious parasitoid
Sclerodermus harmandi in artificial rearing. Biological Control 55: 465-472.
Lockwood, J.L., Cassey, P. & Blackburn, T. 2005. The role of propagule pressure in
explaining species invasions. Trends in Ecology & Evolution 20: 223-228.
Luque, G.M., Vayssade, C., Facon, B., Guillemaud, T., Courchamp, F., Fauvergue, X.
2016. The genetic Allee effect: a unified framework for the genetics and
demography of small populations. Ecosphere. 7(7): e01413. 10.1002/ecs2.1413.
37
Oatman, E.R., Pinto, J.D., Platner, G.R. 1982. Trichogramma (Hymenoptera:
Trichogrammatidae) of Hawaii. Pacific Insects 24: 1-24.
Oostermeijer, J.G.B., Luijten, S.H., den Nijs, J.C.M. 2003. Integrating demographic and
genetic approaches in plant conservation. Biological Conservation 113: 389-398.
Parra, J.R.P. 1997. Técnicas de criação de Anagastakuehniella, hospedeiro alternativo
para produção de Trichogramma. In: Parra, J.R.P., Zucchi, R.A. (eds.),
Trichogramma e o Controle Biológico Aplicad