assessing life history parameters of trissolcusjaponicus

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3. H. Halys female lays eggs 5. Parasitoid forms pupa inside H. Halys egg 6. Adult wasp emerges from pupa 2. Mating 4. Parasitoid searches for egg mass for oviposition At the 28℃ temperature, A. reduvii and T. japonicus females lived longer than males. Similar findings were found for A. bifaciatus (Stahl et al., 2018). The peak period for successful oviposition was 6-10 days after adult emergence for A. reduvii and 2-4 days after adult emergence for T. japonicus. One explanation for these differences between species is that T. japonicus is more synced to the oviposition timing of the H. halys than A. reduvii. Halyomorpha halys is bivoltine in the Mid-Atlantic states. Due to its specialization on H. halys, T. japonicus may more closely track its population dynamics and oviposit in larger numbers during the peak egg load periods of H. halys (generalized life cycle in Fig. 6). Contrarily, A. reduvii it is a generalist parasitoid and as such, is less likely to track H. halys population dynamics. Over time, the female bias in sex ratio showed a decline in T. japonicus. However, both parasitoids had female biased progeny (>1:1). This is speculated to be a response to unlimited host availability causing decreased quality of offspring. According to Hamilton’s local mate competition theory, it is believed that parasitoids exhibit female biased sex ratios because females contain a limited supply of eggs, and ovipositing less males decreases the likelihood that an emerging female will be inseminated by a member of the same egg clutch. One measure of the potential success of using these parasitoids to suppress H. halys is shown in their percent emergence. T. japonicus parasitism rate was 23.8% and A. reduvii was 15.2%. These results look promising for these parasitoids as biological control agents of H. halys. However, more testing is needed to determine their potential for augmentative biological control release programs. Assessing Life History Parameters of Trissolcus japonicus and Anastatus reduvii, Parasitoids of the Brown Marmorated Stink Bug Namitha Thomas, Elizabeth Z. Dabek, Paula M. Shrewsbury, and Cerruti R. R. Hooks Department. of Entomology, University of Maryland, College Park, MD RESULTS INTRODUCTION METHODS This work was supported in part by the USDA National Institute of Food and Agriculture (NIFA), Specialty Crop Research Initiative, award # 2016-51181-25409; and the USDA ARS Areawide IPM Program. The Brown marmorated stink bug, Halyomorpha halys (Stål), is a major agricultural pest. It was first detected in the United States in mid-1990’s and has since spread across Europe and North America (Rice et al., 2014). As part of an integrated effort to manage H. halys, methods of biological control were investigated. Biological control takes advantage of natural enemies such as predators, parasitoids, or pathogens to reduce pest populations. Objectives The goal of this study was to obtain a better understanding of T. japonicus and A. reduvii effectiveness as biological control agents of H. halys by analyzing their life history parameters. Several features measured regarding their longevity and reproduction potential were investigated. Specific factors included: 1) fecundity and progeny emergence, 2) mean lifespan of progeny, and 3) male/female sex ratio of progeny. Parasitoid Rearing Colonies of 25-50 T. japonicus or A. reduvii were maintained in polystyrene containers and kept in growth chambers at 28° C and 66% relative humidity. Parasitoid colonies were fed honey. Experimental Procedure (Fig. 2) 1. Laboratory colonies reared growth chambers. 2. Ten pairs of male and female T. japonicus were placed into independent 10-dram (“F0 vials”). Ten female A. reduvii were separated and placed in F0 vials; female-only due to the inconsistency of A. reduvii producing males within colonies. 3. An egg card containing two frozen H. halys egg masses were placed in each F0 vial. After 48 hrs, egg cards were removed and placed into a separate vial (“F1 vials”) containing progeny. A new egg card was placed in each F0 vial every 48 hours until female death. 4. Progeny emergence vials were checked daily for emerged parasitoids (< 24 hrs in age) and placed into separate vials (“F1 longevity vials”). 5. F1 longevity vials checked daily for mortality. Fig. 2. Layout of laboratory tasks used to measure parasitoid longevity and reproduction potential. Egg Masses (Fig. 3) All egg masses were dissected to measure rates of oviposition and parasitism. Discolored eggs with exit holes were classified as parasitoid emergence (Fig. 3a). Unhatched eggs containing parasitoids inside were classified as non-egressed parasitoids. Eggs with no signs of parasitism were classified as non- parasitized (Fig. 3b). Trissolcus japonicus (Ashmead) is a parasitoid native to South Korea, China, Taiwan and Japan that is now found in the United States (Talamas et. al., 2015). It is known for its short developmental time (Avila & Charles, 2018) and high rates of parasitism of H. halys eggs (Fig. 1a). Trissolcus japonicus is a specialist parasitoid of stink bugs (Pentatomidae). Fig. 1a) Trissolcus japonicus. Photo by Oregon Department of Agriculture Anastatus reduvii (Howard) is a native generalist across orders of insects (Fig. 1b) and is found in the Northeastern United States. It is a major parasitoid of H. halys in Maryland nurseries (Jones et al., 2017). Trissolcus japonicus and A. reduvii are believed to be strong candidates for biological control of H. halys. Fig. 1b) Anastatus reduvii. Photo by Emily Ogburn, NCSU Avila, G. A., & Charles, J. G. (2018). Modelling the potential geographic distribution of Trissolcus japonicus: a biological control agent of the brown marmorated stink bug, Halyomorpha halys. BioControl, 63(4), 505–518. Benelli, G., et. al (2017). The impact of adult diet on parasitoid reproductive performance. Journal of Pest Science, 90(3), 807-823. Force, D. C. (1972). r-and K-strategists in endemic host-parasitoid communities. Bulletin of the ESA, 18(3), 135-137. Jones, A. L, et. al (2017). Field surveys of egg mortality and indigenous egg parasitoids of the brown marmorated stink bug, Halyomorpha halys, in ornamental nurseries in the mid-Atlantic region of the USA. Journal of Pest Science, 90(4), 1159–1168. Lee, J. (1977).Host selection and sex ratio manipulation of solitary hymenopteran parasitoids. Term paper for Michigan State University (online). Leskey, T. C., et. al (2012). Pest status of the brown marmorated stink bug, Halyomorpha halys in the USA. Outlooks on Pest Management, 23(5), 218-226. Nielsen, A. L., & Hamilton, G. C. (2009). Life History of the Invasive Species Halyomorpha halys (Hemiptera: Pentatomidae) in Northeastern United States. Annals of the Entomological Society of America, 102(4), 608-616. Ogburn, E. C., & Walgenbach, J. F. (2019). Effects of Insecticides Used in Organic Agriculture on Anastatus reduvii (Hymenoptera: Eupelmidae) and Telenomus podisi (Hymenoptera: Scelionidae), Egg Parasitoids of Pestivorous Stink Bugs. Journal of economic entomology, 112(1), 108-114. Rice, K. B., et. al (2014). Biology, ecology, and management of brown marmorated stink bug (Hemiptera: Pentatomidae). Journal of Integrated Pest Management, 5(3), A1-A13. Stahl, J., et. al (2018). Life history of Anastatus bifasciatus, a potential biological control agent of the brown marmorated stink bug in Europe. Biological Control. Talamas E. et. al (2015) Trissolcus japonicus (Ashmead) emerges in North America. Journal of Hymenoptera Research 43: 119-128. Ueno, T., & Ueno, K. (2007). The effects of host-feeding on synovigenic egg development in an endoparasitic wasp, Itoplectis naranyae. Journal of insect science (Online), 7, 1–13. Wang, Z. Z., et. al (2019). Parasitoid wasps as effective biological control agents. Journal of Integrative Agriculture, 18(4), 705-715. Progeny Longevity The life history data of A. reduvii and T. japonicus were analyzed using R Statistical Program (RStudio, Inc., 2016) and Excel (Microsoft, 2020). Female progeny of T. japonicus (40.66 ± 0.95 (SE); n =568) lived significantly longer than males (28.13 ± 0.78 (SE); n =504; p = 2.2e-16). Females of A. reduvii lived significantly more days (34.64 ± 0.41 (SE); n =1033) than males (18.96 ± 0.85 (SE); n =134; p = 2.2e-16). In order to quantify the energy cost of oviposition, female F1 individuals, which were not given egg masses were compared to F0 females, which were given egg masses. Female T. japonicus (40.66 ± 0.95 (SE); n=568) lived significantly longer than females who had access to H. halys eggs (23.5 ± 2.03 (SE) days; n =10; p = 3.111e-06). However, female A. reduvii (34.64 ± 0.41 (SE); n =1033) did not live significantly longer than females who had access to H. halys eggs (30± 4.68 (SE) days; n =10; p = 0.2299). Fecundity and Reproductive Rate Fecundity was measured by recording the average number of F1 parasitoids that emerged daily during female F0 lifespan. For T. japonicus F0, peak fecundity was 2-4 days after F0 emergence (maximum=203, minimum=1) (Fig. 4a). The peak fecundity of A. reduvii was 6- 10 days after F0 emergence (maximum=124, minimum=1, Fig. 4b). 0 5 10 15 20 25 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 Average Emerged Progeny Days Alive Average Progeny over Time T. japonicus 0 2 4 6 8 10 12 14 16 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40 Average Emerged Progeny Days Alive Average Progeny over Time A. reduvii Figure 4a, b. The average fecundity of a) T. japonicus and b) A. reduvii F0 females (n=10) during their lifetime. Fecundity was measured by calculating the average number of emerged progeny from egg cards provided to replicate females every two days throughout their lifespan. Male/female Sex Ratio The mean total female to male ratio of T. japonicus F1 parasitoids was 1.3:1. The female to male ratio of A. reduvii F1 parasitoids was 7.7:1. The sex ratio of both T. japonicus (Fig. 5a) and A. reduvii (Fig. 5b) varied over time. 0 2 4 6 8 10 12 14 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 Average Emerged Progeny Days Alive Average Male and Female Emergence over Time of T. japonicus Male Female 0 2 4 6 8 10 12 14 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40 Average Emerged Progeny Days Alive Average Male and Female Emergence over Time of A. reduvii Male Female Figure 5a, b. The average male to female ratio of emerged F1 parasitoids from H. halys eggs parasitized by a) T. japonicus and b) A. reduvii F0 females every two days during their lifetime. Egg fate Egg masses (n=368) were dissected to determine the fate of each egg and classified as parasitoid emergence, non-egressed parasitoid, or non-parasitized. For T. japonicus, progeny successfully emerged from 23.8% of eggs, and 1.4% of eggs contained non-egressed parasitoids. For A. reduvii, progeny successfully emerged from 15.2% of eggs, and 0.5% contained non-egressed parasitoids. Fig. 3a, b. a) Parasitoid emergence and b) non- parasitized eggs. Photo from Jones et. al, 2017 Figure 6. A generalized diagram of a T. japonicus parasitoid life cycle 1 2 3 4 5 1. Adult female parasitoid DISCUSSION ACKNOWLEDGEMENTS a b a b a b a b

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Page 1: Assessing Life History Parameters of Trissolcusjaponicus

3. H. Halys female lays eggs5. Parasitoid forms pupa inside H. Halysegg

6. Adult wasp emerges from pupa 2. Mating

4. Parasitoid searches for egg mass for oviposition

At the 28℃ temperature, A. reduvii and T. japonicus females lived longer than males.Similar findings were found for A. bifaciatus (Stahl et al., 2018). The peak period forsuccessful oviposition was 6-10 days after adult emergence for A. reduvii and 2-4 days afteradult emergence for T. japonicus. One explanation for these differences between species isthat T. japonicus is more synced to the oviposition timing of the H. halys than A. reduvii.Halyomorpha halys is bivoltine in the Mid-Atlantic states. Due to its specialization on H.halys, T. japonicus may more closely track its population dynamics and oviposit in largernumbers during the peak egg load periods of H. halys (generalized life cycle in Fig. 6).Contrarily, A. reduvii it is a generalist parasitoid and as such, is less likely to track H. halyspopulation dynamics.

Over time, the female bias in sex ratio showed a decline in T. japonicus. However, bothparasitoids had female biased progeny (>1:1). This is speculated to be a response tounlimited host availability causing decreased quality of offspring. According to Hamilton’slocal mate competition theory, it is believed that parasitoids exhibit female biased sex ratiosbecause females contain a limited supply of eggs, and ovipositing less males decreases thelikelihood that an emerging female will be inseminated by a member of the same eggclutch.

One measure of the potential success of using these parasitoids to suppress H. halys isshown in their percent emergence. T. japonicus parasitism rate was 23.8% and A. reduviiwas 15.2%. These results look promising for these parasitoids as biological control agentsof H. halys. However, more testing is needed to determine their potential for augmentativebiological control release programs.

Assessing Life History Parameters of Trissolcus japonicus and Anastatus reduvii,Parasitoids of the Brown Marmorated Stink Bug

Namitha Thomas, Elizabeth Z. Dabek, Paula M. Shrewsbury, and Cerruti R. R. HooksDepartment. of Entomology, University of Maryland, College Park, MD

RESULTSINTRODUCTION

METHODS

This work was supported in part by the USDA National Institute of Food and Agriculture(NIFA), Specialty Crop Research Initiative, award # 2016-51181-25409; and the USDAARSAreawide IPM Program.

The Brown marmorated stink bug, Halyomorpha halys (Stål), is a major agriculturalpest. It was first detected in the United States in mid-1990’s and has since spread acrossEurope and North America (Rice et al., 2014). As part of an integrated effort to manageH. halys, methods of biological control were investigated. Biological control takesadvantage of natural enemies such as predators, parasitoids, or pathogens to reduce pestpopulations.

ObjectivesThe goal of this study was to obtain a better understanding of T. japonicus and A. reduviieffectiveness as biological control agents of H. halys by analyzing their life historyparameters. Several features measured regarding their longevity and reproductionpotential were investigated. Specific factors included: 1) fecundity and progenyemergence, 2) mean lifespan of progeny, and 3) male/female sex ratio of progeny.

Parasitoid RearingColonies of 25-50 T. japonicus or A. reduvii were maintained in polystyrene containers and keptin growth chambers at 28° C and 66% relative humidity. Parasitoid colonies were fed honey.

Experimental Procedure (Fig. 2)1. Laboratory colonies reared growth chambers.2. Ten pairs of male and female T. japonicus wereplaced into independent 10-dram (“F0 vials”). Tenfemale A. reduvii were separated and placed in F0 vials;female-only due to the inconsistency of A. reduviiproducing males within colonies.3. An egg card containing two frozen H. halys egg

masses were placed in each F0 vial. After 48 hrs, eggcards were removed and placed into a separate vial(“F1 vials”) containing progeny. A new egg card wasplaced in each F0 vial every 48 hours until femaledeath.4. Progeny emergence vials were checked daily foremerged parasitoids (< 24 hrs in age) and placed intoseparate vials (“F1 longevity vials”).5. F1 longevity vials checked daily for mortality.

Fig. 2. Layout of laboratory tasks used to measure parasitoid longevity and reproduction potential.

Egg Masses (Fig. 3)All egg masses were dissected to measure rates ofoviposition and parasitism. Discolored eggs with exitholes were classified as parasitoid emergence (Fig.3a). Unhatched eggs containing parasitoids insidewere classified as non-egressed parasitoids. Eggswith no signs of parasitism were classified as non-parasitized (Fig. 3b).

Trissolcus japonicus (Ashmead) is a parasitoid native toSouth Korea, China, Taiwan and Japan that is now found inthe United States (Talamas et. al., 2015). It is known for itsshort developmental time (Avila & Charles, 2018) and highrates of parasitism of H. halys eggs (Fig. 1a). Trissolcusjaponicus is a specialist parasitoid of stink bugs(Pentatomidae).Fig. 1a) Trissolcus japonicus. Photo

by Oregon Department of Agriculture

Anastatus reduvii (Howard) is a native generalist across ordersof insects (Fig. 1b) and is found in the Northeastern UnitedStates. It is a major parasitoid of H. halys in Marylandnurseries (Jones et al., 2017). Trissolcus japonicus and A.reduvii are believed to be strong candidates for biologicalcontrol of H. halys. Fig. 1b) Anastatus reduvii. Photo by

Emily Ogburn, NCSU

• Avila, G. A., & Charles, J. G. (2018). Modelling the potential geographic distribution of Trissolcus japonicus: a biological control agent of the brownmarmorated stink bug, Halyomorpha halys. BioControl, 63(4), 505–518.

• Benelli, G., et. al (2017). The impact of adult diet on parasitoid reproductive performance. Journal of Pest Science, 90(3), 807-823.• Force, D. C. (1972). r-and K-strategists in endemic host-parasitoid communities. Bulletin of the ESA, 18(3), 135-137.• Jones, A. L, et. al (2017). Field surveys of egg mortality and indigenous egg parasitoids of the brown marmorated stink bug, Halyomorpha halys, in ornamentalnurseries in the mid-Atlantic region of the USA. Journal of Pest Science, 90(4), 1159–1168.

• Lee, J. (1977).Host selection and sex ratio manipulation of solitary hymenopteran parasitoids. Term paper for Michigan State University (online).• Leskey, T. C., et. al (2012). Pest status of the brown marmorated stink bug, Halyomorpha halys in the USA. Outlooks on Pest Management, 23(5), 218-226.• Nielsen, A. L., & Hamilton, G. C. (2009). Life History of the Invasive Species Halyomorpha halys (Hemiptera: Pentatomidae) in Northeastern United States.Annals of the Entomological Society of America, 102(4), 608-616.

• Ogburn, E. C., & Walgenbach, J. F. (2019). Effects of Insecticides Used in Organic Agriculture on Anastatus reduvii (Hymenoptera: Eupelmidae) and Telenomuspodisi (Hymenoptera: Scelionidae), Egg Parasitoids of Pestivorous Stink Bugs. Journal of economic entomology, 112(1), 108-114.

• Rice, K. B., et. al (2014). Biology, ecology, and management of brown marmorated stink bug (Hemiptera: Pentatomidae). Journal of Integrated PestManagement, 5(3), A1-A13.

• Stahl, J., et. al (2018). Life history of Anastatus bifasciatus, a potential biological control agent of the brown marmorated stink bug in Europe. BiologicalControl.

• Talamas E. et. al (2015) Trissolcus japonicus (Ashmead) emerges in North America. Journal of Hymenoptera Research 43: 119-128.• Ueno, T., & Ueno, K. (2007). The effects of host-feeding on synovigenic egg development in an endoparasitic wasp, Itoplectis naranyae. Journal of insectscience (Online), 7, 1–13.

• Wang, Z. Z., et. al (2019). Parasitoid wasps as effective biological control agents. Journal of Integrative Agriculture, 18(4), 705-715.

Progeny LongevityThe life history data of A. reduvii and T. japonicus were analyzed using R Statistical Program(RStudio, Inc., 2016) and Excel (Microsoft, 2020). Female progeny of T. japonicus (40.66 ±0.95 (SE); n =568) lived significantly longer than males (28.13 ± 0.78 (SE); n =504; p =2.2e-16). Females of A. reduvii lived significantly more days (34.64 ± 0.41 (SE); n =1033)than males (18.96 ± 0.85 (SE); n =134; p = 2.2e-16).

In order to quantify the energy cost of oviposition, female F1 individuals, which were notgiven egg masses were compared to F0 females, which were given egg masses. Female T.japonicus (40.66 ± 0.95 (SE); n=568) lived significantly longer than females who had accessto H. halys eggs (23.5 ± 2.03 (SE) days; n =10; p = 3.111e-06). However, female A. reduvii(34.64 ± 0.41 (SE); n =1033) did not live significantly longer than females who had access toH. halys eggs (30± 4.68 (SE) days; n =10; p = 0.2299).

Fecundity and Reproductive RateFecundity was measured by recording the average number of F1 parasitoids that emergeddaily during female F0 lifespan. For T. japonicus F0, peak fecundity was 2-4 days after F0emergence (maximum=203, minimum=1) (Fig. 4a). The peak fecundity of A. reduvii was 6-10 days after F0 emergence (maximum=124, minimum=1, Fig. 4b).

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Figure 4a, b. The average fecundity of a) T. japonicus and b) A. reduvii F0 females (n=10) during their lifetime. Fecundity was measured bycalculating the average number of emerged progeny from egg cards provided to replicate females every two days throughout their lifespan.

Male/female Sex Ratio The mean total female to male ratio of T. japonicus F1 parasitoids was 1.3:1. The female tomale ratio of A. reduvii F1 parasitoids was 7.7:1. The sex ratio of both T. japonicus (Fig. 5a)and A. reduvii (Fig. 5b) varied over time.

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Figure 5a, b. The average male to female ratio of emerged F1 parasitoids from H. halys eggs parasitized by a) T. japonicus and b) A. reduviiF0 females every two days during their lifetime.

Egg fateEgg masses (n=368) were dissected to determine the fate of each egg and classified asparasitoid emergence, non-egressed parasitoid, or non-parasitized. For T. japonicus, progenysuccessfully emerged from 23.8% of eggs, and 1.4% of eggs contained non-egressedparasitoids. For A. reduvii, progeny successfully emerged from 15.2% of eggs, and 0.5%contained non-egressed parasitoids.Fig. 3a, b. a) Parasitoid emergence and b) non-

parasitized eggs. Photo from Jones et. al, 2017

Figure 6. A generalized diagram of a T. japonicus parasitoid life cycle

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DISCUSSION

ACKNOWLEDGEMENTS

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