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Coffee berry borer (Hypothenemus hampei) 
1 
removal in coffee plantations: 
a pest control service provided by birds 
Alejandra Martínez-Salinas 
Joint Doctoral Program 
CATIE and University of Idaho
(Atlas de Costa Rica, 2005) 
Map: Estrada-Carmona, N. 
3 
• Important crop in 
tropical regions of 
the world (FAO 2007) 
• Overlap with hotspots 
(Moguel and Toledo 1999, Myers et al. 2000) 
• High value for BD conservation, 
especially for bird species, depending 
on management (Perfecto et al. 1996; Greenberg et 
al. 1997a, b; Wunderle and Latta 1998; Cruz- Angón and 
Greenberg 2005) 
ESP Conference / Costa Rica / 2014 
Why the coffee 
berry borer?
ESP Conference / Costa Rica / 2014 4 
Why the coffee 
berry borer? 
• CBB is one if not the most damaging pest 
known to affect coffee crops (Damon 2000; Bustillo 
2006; Vega et al. 2009) 
• Native of central Africa. First record, 
France in 1867 (Damon 2000; Jaramillo et al. 2011) 
• First detected in CR in 2000 now 
nationwide (ICAFE 2011, Staver et al. 2001) 
• Controlled under prescription with 
endosulfan. Highly toxic (Weber et al. 2010) 
http://www.ars.usda.gov
5 
ESP Conference / Costa Rica / 2014
6 
How to measure pest control ? 
• CATIE farm: 1036 ha, 85 ha coffee 
• Pairwise experiment (Exclusions of bird 
activity) 
ESP Conference / Costa Rica / 2014 
25 m 
5m 
50 m 
Excluded 
Not 
excluded 
20m 
Coffee 
plot 
Canopy cover 
10 m 
Brocap® trap
7 
How to measure pest control ? 
• Dynamic of coffee berry borer at the plot level (brocap traps) 
(PROCAFE, Santa Tecla, El Salvador, and CIRAD, Montpellier, France) 
• Bird community at the plot level through fixed radius point 
counts 
• Stomach content samples and faeces (mistnetting) 
Mistnetting protocols 
Emetics (Ipecac, Carapichea ipecacuanha) Diamond et al. (2007) 
Faeces
8 
What have we learn so far?
Brocap® traps collection dates 
Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
Brocap® traps collection dates 
Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
Brocap® traps collection dates 
Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
12 
What have we learn so far? 
• 118 bird species detected 
- 100 (85%) species include invertebrates 
as part of their diet 
- 29 (25%) species exclusively insectivores 
- Only 18 (15%) do not include 
invertebrates as part of their diet 
• 25 (21%) species of Neotropical migrants 
- 11 exclusively insectivore 
- 23 include invertebrates as part of their 
diet. 
ESP Conference / Costa Rica / 2014 
Bird community
13 
What have we learn so far? 
• Infestation rates significantly higher in coffee shrubs 
excluded in comparison with coffee shrubs exposed to 
bird foraging activity (F=23.40, p=0.0019) 
• Positive cbb DNA identification in samples from faeces 
and emesis 
ESP Conference / Costa Rica / 2014 
Exclosures
14 
How to convert this output into an outcome? 
ESP Conference / Costa Rica / 2014
Acknowledgements 
Fabrice DeClerck, PhD Bioversity International 
Kerri Vierling, PhD University of Idaho 
Jacques Avelino, PhD CIRAD 
Lee Vierling, PhD University of Idaho 
University of Idaho (Foster Fellowship) 
IGERT Project (University of Idaho/CATIE/NSF) 
Bird Monitoring Program Volunteers (PMA) 
NMBCA – Borders and Barriers Project 
Natalia Estrada, PhD (Bioversity International) 
Sergio Vilchez (Departamento de Estadística CATIE)
16 
Thank you !
17 
• FAO (Food and Agriculture Organization of the United Nations). 2007. The State of Agricultural Commodity Markets. Rome, Italy, 62 p. 
<http://www.fao.org/publications/soco/en/> (accessed on 11.02.2012). 
• Bustillo, AE. 2006. Una revisión sobre la broca del café, Hypothenemus hampei (Coleoptera: Curculionidae: Scolytinae), en Colombia. Revista Colombiana 
de Entomología. 32(2):101-116. 
• Cruz-Angón, A and Greenberg, R. 2005. Are epiphytes important for birds in coffee plantations? An experimental assessment. Journal of Applied Ecology. 
42:150-159. 
• Damon, A. 2000. A review of the biology and control of the coffee berry borer, Hypothenemus hampei (Coleoptera: Scolytidae). Bulletin of Entomological 
Research. 90:453-465. 
• Diamond, AW; Fayad, VC; McKinley, PS. 2007. Commentary-Ipecac: an improved emetic for wild birds. Journal of Field Ornithology. Vol.78 (4):436-439. 
• Greenberg, R; Bichier, P; Cruz-Angón, A; and Reitsma, R. 1997a. Bird populations in shade and sun coffee plantations in Central Guatemala. Conservation 
Biology. Vol. 11(2):448–459. 
• Greenberg, R; Bichier, P; and Sterling, J. 1997b. Bird populations in rustic and planted shade coffee plantations of Eastern Chiapas, Mexico. Biotropica. Vol. 
29(4):501–514. 
• ICAFE (Costa Rican Institute of Coffee). 2011. Informe sobre la actividad cafetalera de Costa 
Rica.<http://www.icafe.go.cr/sector_cafetalero/estadsticas/infor_activ_cafetal/actual/Informe%20Actividad%20Cafetalera%202011.pdf>(accessed 
11.03.2012). 
• Jaramillo, J; Muchugu, E; Vega, FE; Davis, A; Borgemeister, C; Chabi-Olaye, A. 2011. Some Like it Hot: The influence and implications of climate change on 
coffee berry borer (Hypothenemus hampei) and coffee production in East Africa. PLoS ONE 6(9): e24528. doi:10.1371/journal.pone.0024528 
• Johnson, MD; Kellermann, JL; Stercho, AM. 2010. Pest reduction services by birds in shade and sun coffee in Jamaica. Animal Conservation. Vol. 13:140- 
147. 
• Karp, DS; Mendenhall, CD; Figueroa Sandi, R; Chaumont, N; Ehrlich, PR; Hadly, EA; Daily, G. 2013. Forest bolsters bird abundance, pest control and coffee 
yield. Ecology Letters. 
• Kellermann JL; Johnson, MD; Stercho, AM; Hackett, SC. 2008. Ecological and economic services provided by birds on Jamaican blue mountain coffee farms. 
Conservation Biology. Vol. 22(5):1177-1185. 
• Moguel, P and Toledo, VM. 1999. Biodiversity conservation in traditional coffee systems of Mexico. Conservation Biology. Vol. 13(1):11-21. 
• Myers, N; Mittermeier, RA; Mittermeier, CG; da Fonseca, GAB; Kent, J. 2000. Biodiversity hotspots for conservation priorities. Nature. Vol. 403:853-858. 
• Perfecto, I; Rice, RA; Greenberg, R; Van Der Voort, ME. 1996. Shade coffee: a disappearing refuge for biodiversity. BioScience. Vol. 46(8): 598-608. 
• Staver, C., F. Guharay, D. Monterroso, and R. G. Muschler. 2001. Designing pest-suppressive multistrata perennial crop systems: shade-grown coffee in 
Central America. Agroforestry Systems 53:151–170. 
• Vega, FE; Infante, F; Castillo, A; Jaramillo, J. 2009. The coffee berry borer, Hypothenemus hampei (Ferrari) (Coleoptera: Curculionidae): a short review, with 
recent findings and future research directions. Terrestrial Arthropod Reviews 2:129-147. 
• Weber, J; Halsall, CJ; Muir, D; Teixeira, C; Small, J; Solomon, K; Hermanson, M; Hung, H; Bidleman, T. 2010. Endosulfan, a global pesticide: A review of its 
fate in the environment and occurrence in the Arctic. Science of the Total Environment. 408:2966-2984. 
• Wunderle, JM; Latta, SC. 1998. Avian resource use in dominican shade coffee plantations. Wilson Bulletin 110(2):271-281.

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Coffee berry borer (Hypothenemus hampei) removal in coffee plantations: a pest control service provided by birds

  • 1. Coffee berry borer (Hypothenemus hampei) 1 removal in coffee plantations: a pest control service provided by birds Alejandra Martínez-Salinas Joint Doctoral Program CATIE and University of Idaho
  • 2.
  • 3. (Atlas de Costa Rica, 2005) Map: Estrada-Carmona, N. 3 • Important crop in tropical regions of the world (FAO 2007) • Overlap with hotspots (Moguel and Toledo 1999, Myers et al. 2000) • High value for BD conservation, especially for bird species, depending on management (Perfecto et al. 1996; Greenberg et al. 1997a, b; Wunderle and Latta 1998; Cruz- Angón and Greenberg 2005) ESP Conference / Costa Rica / 2014 Why the coffee berry borer?
  • 4. ESP Conference / Costa Rica / 2014 4 Why the coffee berry borer? • CBB is one if not the most damaging pest known to affect coffee crops (Damon 2000; Bustillo 2006; Vega et al. 2009) • Native of central Africa. First record, France in 1867 (Damon 2000; Jaramillo et al. 2011) • First detected in CR in 2000 now nationwide (ICAFE 2011, Staver et al. 2001) • Controlled under prescription with endosulfan. Highly toxic (Weber et al. 2010) http://www.ars.usda.gov
  • 5. 5 ESP Conference / Costa Rica / 2014
  • 6. 6 How to measure pest control ? • CATIE farm: 1036 ha, 85 ha coffee • Pairwise experiment (Exclusions of bird activity) ESP Conference / Costa Rica / 2014 25 m 5m 50 m Excluded Not excluded 20m Coffee plot Canopy cover 10 m Brocap® trap
  • 7. 7 How to measure pest control ? • Dynamic of coffee berry borer at the plot level (brocap traps) (PROCAFE, Santa Tecla, El Salvador, and CIRAD, Montpellier, France) • Bird community at the plot level through fixed radius point counts • Stomach content samples and faeces (mistnetting) Mistnetting protocols Emetics (Ipecac, Carapichea ipecacuanha) Diamond et al. (2007) Faeces
  • 8. 8 What have we learn so far?
  • 9. Brocap® traps collection dates Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
  • 10. Brocap® traps collection dates Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
  • 11. Brocap® traps collection dates Total number of coffee berry borer (Hypothenemus hampei) trapped in Brocap® traps
  • 12. 12 What have we learn so far? • 118 bird species detected - 100 (85%) species include invertebrates as part of their diet - 29 (25%) species exclusively insectivores - Only 18 (15%) do not include invertebrates as part of their diet • 25 (21%) species of Neotropical migrants - 11 exclusively insectivore - 23 include invertebrates as part of their diet. ESP Conference / Costa Rica / 2014 Bird community
  • 13. 13 What have we learn so far? • Infestation rates significantly higher in coffee shrubs excluded in comparison with coffee shrubs exposed to bird foraging activity (F=23.40, p=0.0019) • Positive cbb DNA identification in samples from faeces and emesis ESP Conference / Costa Rica / 2014 Exclosures
  • 14. 14 How to convert this output into an outcome? ESP Conference / Costa Rica / 2014
  • 15. Acknowledgements Fabrice DeClerck, PhD Bioversity International Kerri Vierling, PhD University of Idaho Jacques Avelino, PhD CIRAD Lee Vierling, PhD University of Idaho University of Idaho (Foster Fellowship) IGERT Project (University of Idaho/CATIE/NSF) Bird Monitoring Program Volunteers (PMA) NMBCA – Borders and Barriers Project Natalia Estrada, PhD (Bioversity International) Sergio Vilchez (Departamento de Estadística CATIE)
  • 17. 17 • FAO (Food and Agriculture Organization of the United Nations). 2007. The State of Agricultural Commodity Markets. Rome, Italy, 62 p. <http://www.fao.org/publications/soco/en/> (accessed on 11.02.2012). • Bustillo, AE. 2006. Una revisión sobre la broca del café, Hypothenemus hampei (Coleoptera: Curculionidae: Scolytinae), en Colombia. Revista Colombiana de Entomología. 32(2):101-116. • Cruz-Angón, A and Greenberg, R. 2005. Are epiphytes important for birds in coffee plantations? An experimental assessment. Journal of Applied Ecology. 42:150-159. • Damon, A. 2000. A review of the biology and control of the coffee berry borer, Hypothenemus hampei (Coleoptera: Scolytidae). Bulletin of Entomological Research. 90:453-465. • Diamond, AW; Fayad, VC; McKinley, PS. 2007. Commentary-Ipecac: an improved emetic for wild birds. Journal of Field Ornithology. Vol.78 (4):436-439. • Greenberg, R; Bichier, P; Cruz-Angón, A; and Reitsma, R. 1997a. Bird populations in shade and sun coffee plantations in Central Guatemala. Conservation Biology. Vol. 11(2):448–459. • Greenberg, R; Bichier, P; and Sterling, J. 1997b. Bird populations in rustic and planted shade coffee plantations of Eastern Chiapas, Mexico. Biotropica. Vol. 29(4):501–514. • ICAFE (Costa Rican Institute of Coffee). 2011. Informe sobre la actividad cafetalera de Costa Rica.<http://www.icafe.go.cr/sector_cafetalero/estadsticas/infor_activ_cafetal/actual/Informe%20Actividad%20Cafetalera%202011.pdf>(accessed 11.03.2012). • Jaramillo, J; Muchugu, E; Vega, FE; Davis, A; Borgemeister, C; Chabi-Olaye, A. 2011. Some Like it Hot: The influence and implications of climate change on coffee berry borer (Hypothenemus hampei) and coffee production in East Africa. PLoS ONE 6(9): e24528. doi:10.1371/journal.pone.0024528 • Johnson, MD; Kellermann, JL; Stercho, AM. 2010. Pest reduction services by birds in shade and sun coffee in Jamaica. Animal Conservation. Vol. 13:140- 147. • Karp, DS; Mendenhall, CD; Figueroa Sandi, R; Chaumont, N; Ehrlich, PR; Hadly, EA; Daily, G. 2013. Forest bolsters bird abundance, pest control and coffee yield. Ecology Letters. • Kellermann JL; Johnson, MD; Stercho, AM; Hackett, SC. 2008. Ecological and economic services provided by birds on Jamaican blue mountain coffee farms. Conservation Biology. Vol. 22(5):1177-1185. • Moguel, P and Toledo, VM. 1999. Biodiversity conservation in traditional coffee systems of Mexico. Conservation Biology. Vol. 13(1):11-21. • Myers, N; Mittermeier, RA; Mittermeier, CG; da Fonseca, GAB; Kent, J. 2000. Biodiversity hotspots for conservation priorities. Nature. Vol. 403:853-858. • Perfecto, I; Rice, RA; Greenberg, R; Van Der Voort, ME. 1996. Shade coffee: a disappearing refuge for biodiversity. BioScience. Vol. 46(8): 598-608. • Staver, C., F. Guharay, D. Monterroso, and R. G. Muschler. 2001. Designing pest-suppressive multistrata perennial crop systems: shade-grown coffee in Central America. Agroforestry Systems 53:151–170. • Vega, FE; Infante, F; Castillo, A; Jaramillo, J. 2009. The coffee berry borer, Hypothenemus hampei (Ferrari) (Coleoptera: Curculionidae): a short review, with recent findings and future research directions. Terrestrial Arthropod Reviews 2:129-147. • Weber, J; Halsall, CJ; Muir, D; Teixeira, C; Small, J; Solomon, K; Hermanson, M; Hung, H; Bidleman, T. 2010. Endosulfan, a global pesticide: A review of its fate in the environment and occurrence in the Arctic. Science of the Total Environment. 408:2966-2984. • Wunderle, JM; Latta, SC. 1998. Avian resource use in dominican shade coffee plantations. Wilson Bulletin 110(2):271-281.

Editor's Notes

  1. CATIE – Tropical Agricultural Research and Higher Education Center
  2. Regulating Services – Pest control Ecosystem services is a human centered concept and so ES are not ES until we linked them directly with humans ! Bird species which provide us with an array of ecosystem services including seed dispersal, pollination, and pest control. Regulating ecosystem services such as pest control (MEA 2005) are especially important to quantify because their benefits can be perceived at smaller scales and directly by coffee growers.
  3. CR has 909 species based on the CR Ornithological Association / Species List 2013
  4. Complete life cycle takes from 28 to 34 days (4 (egg), 15 (larva), 7 (pupa)) (Damon 2000, Vega et al. 2009) Females may lay between 31 to 119 eggs in a single suitable coffee berry. The complete life cycle may take up to 28 to 34 days. Males may live 20-87 days and females may live on average 157 days (Barrera 1994 cited by Damon 2000). Where coffee is present all year round (Uganda / Turrialba), H. hampei may exceed eight generations a year (Hargreaes 1926 cited by Damon 2000). Only females fly and wing muscles seem to degenerate when egg laying starts preventing them to colonize other berries (Ticheler 1991 cited by Damon 2000). cbb feeds on and reproduces in the endosperm of the coffee seed. Drilling of a berry in optimum conditions may take up to 8 hours. During this time is vulnerable to pest control agents.
  5. The coffee berry borer will eat the endosperm of the coffee berry, lay eggs and stayed there until an environmental stimuli drives them to find new available berries to colonize.
  6. A total of 48 bird species were detected with both sampling methods. Out of the 118 bird species detected 100 (85%) species include invertebrates as part of their diet; 67 (57%) species are insectivores but include small fruits, seeds, nectar and others as part of their diet; 29 (25%) species are exclusively insectivores and only 18 (15%) species do not include invertebrates as part of their diets. From this total 93 species are classified as resident and 25 as Neotropical migrants. Out of the 25 species of Neotropical migrants, 11 species are exclusively insectivore and 23 include invertebrates as part of their diet.
  7. A total of 48 bird species were detected with both sampling methods. Out of the 118 bird species detected 100 (85%) species include invertebrates as part of their diet; 67 (57%) species are insectivores but include small fruits, seeds, nectar and others as part of their diet; 29 (25%) species are exclusively insectivores and only 18 (15%) species do not include invertebrates as part of their diets. From this total 93 species are classified as resident and 25 as Neotropical migrants. Out of the 25 species of Neotropical migrants, 11 species are exclusively insectivore and 23 include invertebrates as part of their diet.
  8. CIRAD (French Agricultural Research for Development) – A French research centre working with developing countries to tackle agricultural and development issues