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Dual regime shifts in dynamics of an 
invasive predator 
are linked to the invasion and insecticidal 
control of its prey 
Christine A. Bahlai1, Wopke vander 
Werf2, Matthew O’Neal3, Lia 
Hemerik2, Douglas A. Landis1 
1 Michigan State University 
2 Wageningen University 
3 Iowa State University
Regime shifts 
 Substantial, persistent changes in function of an 
ecosystem function or process 
 Example: Zebra muscles in Great Lakes drive 
dramatic shifts phytoplankton communities 
 Dynamics of prey can dramatically 
shift the population dynamics in 
predatory species 
USGS 
Scheffer, M., S. Carpenter, J. A. Foley, C. Folke, and B. Walker. 2001. Catastrophic shifts in ecosystems. Nature 413:591- 
596. 
Strayer, D. L. 2008. Twenty years of zebra mussels: lessons from the mollusk that made headlines. Frontiers in Ecology and 
the Environment 7:135-141.
Population regulation in Harmonia 
Knapp, A. K., et al. 2012. Past, present, and future roles of long-term experiments in the LTER Network. Bioscience 62:377- 
389.
Model selection 
 Fit Ricker model to population 
time series 
 Allow K and r to vary 
 Use AIC to determine best fit 
Population this year 
푵 풕 + ퟏ = 푵 풕 풆풙풑 풓 ퟏ − 
푵 풕 
푲 
Population next year 
Per capita rate of increase 
Bruce E. Kendall, W. M. Schaffer, C. W. Tidd, 
and Lars F. Olsen. The Impact of Chaos on 
Science and Society (UNU; 1997; 394 pages) 
Carrying capacity
1996 
1995 
0.6 
0.4 
1994 
2001 
1997 
1998 
2000 
1999 
2002 
2003 
2004 
2005 
2006 
2007 
2008 
2009 
2010 
2011 
2012 
0.2 
0.0 0.2 0.4 0.6 
N(t) 
N(t+1) 
phase 
A 
B 
C
Harmonia dynamics 
0.6 
0.4 
0.2 
0.0 
1995 2000 2005 2010 
Year 
Average captures per trap 
phase 
A 
B 
C 
Same r and 
K? 
 Arrival of soybean aphid (2000) induced shift in Harmonia’s 
dynamic regime 
 r +20%, K +40% 
 What caused return to previous regime after 2005?
Soybean aphid 
State 
2000 
2001 
2002 
2003 
2004 
2005 
2006 
2007 
2008 
No more major 
outbreaks in MI 
2009 
2010 
2011 
2012 
Michigan 
Iowa 
Illinois 
Wisconsi 
n 
Low Spotty Moderate High 
No aphids Widespread outbreaks
Pesticide use 
0.004 
0.003 
0.002 
0.001 
0.000 
Cyhalothrin-lambda 
2000 2004 2008 
0.003 
0.002 
0.001 
0.000 
Esfenvalerate 
2000 2004 2008 
0.020 
0.015 
0.010 
0.005 
0.000 
Imidacloprid 
2000 2004 2008 
0.015 
0.010 
0.005 
0.000 
Thiamethoxam 
2000 2004 2008 
State 
Year 
kg active ingredient per hectare 
2008 
2008 
2008 
Stone, W. W. 2013. Estimated Annual 
Agricultural Pesticide Use for Counties of 
the Conterminous United States, 1992– 
2009. U.S. Geological Survey Data Series 
752:http://pubs.usgs.gov/ds/752/. 
2008 
State 
IA 
IL 
MI 
WI 
Foliar Seed applied
Seed treatments and soybean aphid 
 Seed treatments: limited window of efficacy 
(~40DAP) 
0 DAP 40 DAP 
 Early season suppression leads to regional control? 
Aphid populations 
Time 
EIL 
Johnson, K. D., M. E. O'Neal, D. W. Ragsdale, C. D. Difonzo, S. M. Swinton, P. M. Dixon, B. D. Potter, E. W. Hodgson, and A. 
C. Costamagna. 2009. Probability of cost-effective management of soybean aphid (Hemiptera: Aphididae) in North America. 
Journal of Economic Entomology 102:2101-2108.
Aphid infestation vs pesticide use 
0.004 
0.003 
0.002 
0.001 
Cyhalothrin-lambda 
Low Spotty Moderate High 
0.0025 
0.0020 
0.0015 
0.0010 
0.0005 
0.0000 
Esfenvalerate 
Low SpottyModerate High 
0.020 
0.015 
0.010 
0.005 
0.000 
Imidacloprid 
Low Spotty Moderate High 
0.010 
0.005 
0.000 
Thiamethoxam 
Low SpottyModerate High 
Aphid infestation 
kg active ingredient per hectare
Conclusions 
 Soybean aphid is less abundant at a regional scale 
since the introduction of neonicotinoid seed treatments 
 Harmonia dynamics are indistinguishable from their 
dynamics before soybean aphid’s arrival. 
 Agricultural management has driven a regime shift
Implications 
 Neonicotinoid regulation-a 
changing landscape? 
 Can we maintain 
landscape-level 
suppression of two 
invasives? 
 Resistant soybean Rag 
genes- season long 
suppression 
Myers, C. and E. Hill. 2014. Benefits of neonicotinoid seed treatments to 
soybean production. United States Environmental Protection Agency. 
http://www2.epa.gov/pollinator-protection/benefits-neonicotinoid-seed-treatments- 
soybean-production. 
Hallmann, C. A. et al . 2014. Declines in insectivorous birds are associated 
with high neonicotinoid concentrations. Nature advance online 
publication. 
Blacquière, T., G. Smagghe, C. M. van Gestel, and V. Mommaerts. 2012. 
Neonicotinoids in bees: a review on concentrations, side-effects and risk 
assessment. Ecotoxicology 21:973-992.
Metadata 
 @cbahlai 
https://github.com/cbahlai/LTER_Ladybeetle_Ricke 
r 
 Data sources: 
 Cooperative Extension (MSU, ISU, UI, UW- aphid 
scouting data) 
 Doug Landis, Stuart Gage, Manuel Colunga-Garcia 
(MSU-ladybeetle data) 
 Wesley Stone (USGS- Pesticide data) 
 USDA-NASS (Crop production data)
Acknowledgements 
 Data creators 
 J. Megan Woltz and Julia Perrone 
 Funding agencies

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Dual regime shifts in dynamics of an invasive predator entsoc 14

  • 1. Dual regime shifts in dynamics of an invasive predator are linked to the invasion and insecticidal control of its prey Christine A. Bahlai1, Wopke vander Werf2, Matthew O’Neal3, Lia Hemerik2, Douglas A. Landis1 1 Michigan State University 2 Wageningen University 3 Iowa State University
  • 2. Regime shifts  Substantial, persistent changes in function of an ecosystem function or process  Example: Zebra muscles in Great Lakes drive dramatic shifts phytoplankton communities  Dynamics of prey can dramatically shift the population dynamics in predatory species USGS Scheffer, M., S. Carpenter, J. A. Foley, C. Folke, and B. Walker. 2001. Catastrophic shifts in ecosystems. Nature 413:591- 596. Strayer, D. L. 2008. Twenty years of zebra mussels: lessons from the mollusk that made headlines. Frontiers in Ecology and the Environment 7:135-141.
  • 3. Population regulation in Harmonia Knapp, A. K., et al. 2012. Past, present, and future roles of long-term experiments in the LTER Network. Bioscience 62:377- 389.
  • 4. Model selection  Fit Ricker model to population time series  Allow K and r to vary  Use AIC to determine best fit Population this year 푵 풕 + ퟏ = 푵 풕 풆풙풑 풓 ퟏ − 푵 풕 푲 Population next year Per capita rate of increase Bruce E. Kendall, W. M. Schaffer, C. W. Tidd, and Lars F. Olsen. The Impact of Chaos on Science and Society (UNU; 1997; 394 pages) Carrying capacity
  • 5. 1996 1995 0.6 0.4 1994 2001 1997 1998 2000 1999 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 0.2 0.0 0.2 0.4 0.6 N(t) N(t+1) phase A B C
  • 6. Harmonia dynamics 0.6 0.4 0.2 0.0 1995 2000 2005 2010 Year Average captures per trap phase A B C Same r and K?  Arrival of soybean aphid (2000) induced shift in Harmonia’s dynamic regime  r +20%, K +40%  What caused return to previous regime after 2005?
  • 7. Soybean aphid State 2000 2001 2002 2003 2004 2005 2006 2007 2008 No more major outbreaks in MI 2009 2010 2011 2012 Michigan Iowa Illinois Wisconsi n Low Spotty Moderate High No aphids Widespread outbreaks
  • 8. Pesticide use 0.004 0.003 0.002 0.001 0.000 Cyhalothrin-lambda 2000 2004 2008 0.003 0.002 0.001 0.000 Esfenvalerate 2000 2004 2008 0.020 0.015 0.010 0.005 0.000 Imidacloprid 2000 2004 2008 0.015 0.010 0.005 0.000 Thiamethoxam 2000 2004 2008 State Year kg active ingredient per hectare 2008 2008 2008 Stone, W. W. 2013. Estimated Annual Agricultural Pesticide Use for Counties of the Conterminous United States, 1992– 2009. U.S. Geological Survey Data Series 752:http://pubs.usgs.gov/ds/752/. 2008 State IA IL MI WI Foliar Seed applied
  • 9. Seed treatments and soybean aphid  Seed treatments: limited window of efficacy (~40DAP) 0 DAP 40 DAP  Early season suppression leads to regional control? Aphid populations Time EIL Johnson, K. D., M. E. O'Neal, D. W. Ragsdale, C. D. Difonzo, S. M. Swinton, P. M. Dixon, B. D. Potter, E. W. Hodgson, and A. C. Costamagna. 2009. Probability of cost-effective management of soybean aphid (Hemiptera: Aphididae) in North America. Journal of Economic Entomology 102:2101-2108.
  • 10. Aphid infestation vs pesticide use 0.004 0.003 0.002 0.001 Cyhalothrin-lambda Low Spotty Moderate High 0.0025 0.0020 0.0015 0.0010 0.0005 0.0000 Esfenvalerate Low SpottyModerate High 0.020 0.015 0.010 0.005 0.000 Imidacloprid Low Spotty Moderate High 0.010 0.005 0.000 Thiamethoxam Low SpottyModerate High Aphid infestation kg active ingredient per hectare
  • 11. Conclusions  Soybean aphid is less abundant at a regional scale since the introduction of neonicotinoid seed treatments  Harmonia dynamics are indistinguishable from their dynamics before soybean aphid’s arrival.  Agricultural management has driven a regime shift
  • 12. Implications  Neonicotinoid regulation-a changing landscape?  Can we maintain landscape-level suppression of two invasives?  Resistant soybean Rag genes- season long suppression Myers, C. and E. Hill. 2014. Benefits of neonicotinoid seed treatments to soybean production. United States Environmental Protection Agency. http://www2.epa.gov/pollinator-protection/benefits-neonicotinoid-seed-treatments- soybean-production. Hallmann, C. A. et al . 2014. Declines in insectivorous birds are associated with high neonicotinoid concentrations. Nature advance online publication. Blacquière, T., G. Smagghe, C. M. van Gestel, and V. Mommaerts. 2012. Neonicotinoids in bees: a review on concentrations, side-effects and risk assessment. Ecotoxicology 21:973-992.
  • 13. Metadata  @cbahlai https://github.com/cbahlai/LTER_Ladybeetle_Ricke r  Data sources:  Cooperative Extension (MSU, ISU, UI, UW- aphid scouting data)  Doug Landis, Stuart Gage, Manuel Colunga-Garcia (MSU-ladybeetle data)  Wesley Stone (USGS- Pesticide data)  USDA-NASS (Crop production data)
  • 14. Acknowledgements  Data creators  J. Megan Woltz and Julia Perrone  Funding agencies