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Effe ffect of of Bac acillus lar arvicide deon on em emer ergent nt aq aqua uatic Chi Chirono nomidae in n a a tem temperate-wetlan and ec ecos osystem (Otta ttawa, a, Cana Canada) LIAM J. EPP U OTTAWA 2019 Non-target


  1. Effe ffect of of Bac acillus – lar arvicide deon on em emer ergent nt aq aqua uatic Chi Chirono nomidae in n a a tem temperate-wetlan and ec ecos osystem (Otta ttawa, a, Cana Canada) LIAM J. EPP U OTTAWA 2019

  2. Non-target Organisms: Chi Chironomidae • Broad Spectrum vs. Selective insecticides • May harm non non-ta target t organism sms s (NTO) O) 4,5,6,7 • Chironomidae are closely related to mosquitoes (Culici cidae) Insecta Nematocera • Dominate wetland insect communities 2 3 • > 65 species in Ontario wetlands • Re Remova val would disr srupt or shift trophic c relationsh ships s 9,10,11 2 Lepper & Taylor (1998), 3 Webb (1969), 4 Dickman (2000), 5 Hershey et al. (1998), 6 Lundstrӧm et al. (2010b), 7 Lagadic et al. (2016), 8 Poulin (2012), 9 Lundstr ӧ m et al. (2010a), 10 Östman et al. (2008); 11 Duguma et al. (2015), Photo: Toronto Star

  3. Non-target Organisms: Chi Chironomidae • Broad Spectrum vs. Selective insecticides • May harm non non-ta target t organism sms s (NTO) O) 4,5,6,7 • Chironomidae are closely related to mosquitoes (Culici cidae) Insecta Nematocera • Dominate wetland insect communities 2 3 • > 65 species in Ontario wetlands • Re Remova val would disr srupt or shift trophic c relationsh ships s 9,10,11

  4. Expe periment ntal Des Design Emerg rgence ce Tra rap SOUTH MARCH HIGHLANDS CARP (CTRL) CONSERVATION FOREST (BTI/BTI2) • 15 15 BTI-tr treate ted (red) in Kanata & 15 CTRL ponds (green) near Carp • 9 9 BTI-tr treate ted, , 6 BTI2 (yellow) previously treated & 15 CTRL ponds

  5. Results

  6. Chironom ronomidae dae Emergenc ergence (y+1)) 1)) 10 (y og 10 e (log ance undanc Abund May Sept Week ek of Year ear CHI Individuals/Site/Week: 25.9 (BTI) & 38.7 (CTRL) 2018 p=0.003

  7. Direc rect effec ects? Treatment Period Mid- June → August (May → Mid -June) CHIRONOMIDAE CULICIDAE

  8. Annual nual Chiro ronom nomidae dae Emerge ergenc nce 1)) (y+1)) 10 (y og 10 e (log undance Abundanc

  9. Redun dundanc ancy Anal nalysis: Combi bini ning ng Emerge ergenc nce e with h Env nvironm ronment ent ALL YEARS Ento & Environ Triplot RDA 1.0 BTI BTI2 Water.Temperature..Celcius CTRL 0.5 Average.Water.Depth..cm CHI CHI COL ARA RDA2 Conductivity..uS.cm OTH DIP HYM EPH ORT 0.0 ODO PLE HEM LEP CUL CUL -0.5 BOL -1.0 -2 -1 0 1 2 RDA1 • GLMM → Linear Modeling that accounted for intra -site variability dropped TREATMENT EFFECT in all models!

  10. Biodi divers Species/ Taxa- Richness Shannon Diversity ersity P= 0.057

  11. Conc Conclusion • Differences observed in Chironomidae counts are statistically attributed to DEPTH & other factors • Bti – effect was systematically removed from best-fit CHI emergence response models • Elevated Biodiversity in 2018 at BTI sites • Consistent increases in CHI counts suggest no shortage of food for insectivores

  12. Questio ions? Thank you!

  13. Supplementary Material

  14. ARA CHI COL 0.7 0.6 0.5 1.0 0.5 0.4 0.9 0.8 0.4 CUL DIP EPH 0.7 1.0 Abundance [log10(y+1)] Treatment 1.0 BTI 0.5 BTI2 0.5 CTRL 0.7 0.4 0.6 0.3 HYM LEP ODO 0.7 0.6 0.5 0.5 0.4 0.4 0.3 0.3 2016 2017 2018 2016 2017 2018 2016 2017 2018 Year

  15. Dissolved.Oxygen..mg.L pH Conductivity..uS.cm 80 1500 8 60 7 1000 6 40 5 500 20 4 3 0 0 15 20 25 30 35 40 15 20 25 30 35 40 15 20 25 30 35 40 Water.Temperature..Celcius Average.Water.Depth..cm Ammonia.NH3..mg.L Measurement 30 60 Year 2 2016 40 20 2017 1 20 2018 10 0 0 15 20 25 30 35 40 15 20 25 30 35 40 15 20 25 30 35 40 Nitrate.NO3..mg.L Sulphate.SO4..mg.L Surface.Area..m2 2.0 90000 20 1.5 60000 1.0 10 30000 0.5 0.0 0 0 15 20 25 30 35 40 15 20 25 30 35 40 15 20 25 30 35 40 Year

  16. Refe References 1-7 7 (of of 13 13) 1 World Health Organization (1999). Microbial Pest Control Agent Bacillus thuringiensis (Environmental Health Criteria 217). Geneva, Switzerland. Retrieved from http://www.who.int/ipcs/publications/ehc/en/EHC217.PDF 2 Leeper, D.A. & Taylor, B.E. (1998). Insect Emergence from a South Carolina (USA) Temporary Wetland Pond, with Emphasis on the Chironomidae (Diptera). J. N. Am. Benthol. Soc ., 17(1):54-72. 3 Webb, D.W. (1969). Production of wetland Chironomidae (Diptera) and the effects of using Bacillus thuringiensis israelensis for mosquito control. Journal of the Kansas Entomological Society , 42(1), 91- 108. 4 Dickman, M. (2000). Impacts of a mosquito selective pesticide, Bti , on the macroinvertebrates of a subtropical stream in Hong Kong. Chemosphere, 41, 209-217. 5 Hershey, A.E., Lima, A.R., Niemi, G.J. & Regal, R.R. (1998). Effects of Bacillus thuringiensis israelensis Bti and methoprene on nontarget macroinvertebrates in Minnesota wetlands. Ecological Applications, 8, 41-60. 6 Lundstrӧm, J.O., Schӓfer, M.L., Petersson, E., Persson Vinnersten, T.Z., Landin, J. & Brodin, Y. (2010b). Production of wetland Chironomidae (Diptera) and the effects of using Bacillus thuringiensis israelensis for mosquito control. Bulletin of Entomological Research , 100, 117-125. doi:10.1017/S0007485309990137. 7 Lagadic, L., Schäfer, R.B., Roucaute, M., Szöcs, E., Chouin, S., de Maupeouc, J., Duchet C., Franquet, E., Hunsec, B.L., Bertrand, C., Fayolle S., Francés, B., Rozier, Y., Foussadier, R., Santoni, J.B. & Lagneau, C. (2016). No association between the use of Bti for mosquito control and the dynamics of non-target aquatic invertebrates in French coastal and continental wetlands. Science of the Total Environment , 553, 486 – 494. http://dx.doi.org/10.1016/j.scitotenv.2016.02. 096.et al. (2016),

  17. Refe References 8-15 15 (of of 15 15) 8 Poulin, B. (2012). Indirect effects of bioinsecticides on the nontarget fauna: The Camargue experiment calls for future research. Acta Oecologica , 44, 28-32 doi:10.1016/j.actao. 2011.11.005. 9 Lundström, J.O., Brodin, Y., Schäfer, M.L., Vinnersten, T.Z.P. & Östman, Ö. (2010a). High species richness of Chironomidae (Diptera) in temporary flooded wetlands associated with high species turn-over rates. Bulletin of Entomological Research , 100(4), 433 – 444. doi: 10.1017/S0007485309990472. 10 Östman, O., Lundstrӧm, J.O. & Persson Vinnersten, T.Z. (2008). Effects of mosquito larvae removal with Bacillus 10 thuringiensis israelensis ( Bti ) on natural protozoan communities. Hydrobiologia , 607, 231-235. doi: 10.1007/s10750-008- 9387-z. 11 Duguma, D., Hall, M.W., Rugman-Jones, P., Stouthamer. R., Neufeld, J.D. & Walton, W.E. (2015). Microbial 11 communities and nutrient dynamics in experimental microcosms are altered after the application of a high dose of Bti . Journal of Applied Ecology , 52, 763 – 773. doi: 10.1111/1365-2664.12422. 12 12 Government of Canada. (2016). Climate data [Daily Data Report for 2016]. Ottawa, Ontario, Canada. Retrieved from: http://climate.weather.gc.ca/climate_data/daily_data_e.html? StationID =49568 13 13 Government of Canada. (2017). Climate data [Daily Data Report for 2017]. Ottawa, Ontario, Canada. Retrieved from: http://climate.weather.gc.ca/climate_data/daily_data_e.html? StationID =49568 14 Zheng, M.-L., Zhang, D.-J., Damiens, D. D., Lees, R.S. & Gilles, J.R.L. (2015). Standard operating procedures for 14 standardized mass rearing of the dengue and chikungunya vectors Aedes aegypti and Aedes albopictus (Diptera: Culicidae) - II - Egg storage and hatching. Parasites & Vectors, 8, 348. http://doi.org/10.1186/s13071-015-0951-x Photo (Slide 6):The Toronto Star https://www.thestar.com/news/gta/2009/05/22/clouds_of_midges_thats_just_bug_love.html

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