Impact of Neotropical Wet Forest Restoration on the ... Stevenson SACNAS...presentation of this...

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Arthropods are considered ecosystem engineers and are essential to the brown food web as they transform the soil by consuming plant debris and depositing feces that serve as food sources for micro- organisms, therefore, fostering microbial population growth and dispersal. This research aimed to assess how restoration stages affect arthropod populations and to validate the alternative state hypothesis. Arthropod abundance was significantly higher in primary forest compared to other forests at different restoration stages: Evolutionary history of plant communities in this forest type favors arthropod population growth (Dinnage et al. 2012). When focusing solely on the predatory arthropod community, the abundance difference across habitat type was not significant: Tree species diversity does not have an effect on predatory arthropod abundance (Vehvilainem et al. 2008). These findings offer a useful foundation to better address ground-dwelling organisms in reforestation efforts in the Neotropics as they partially validate the alternative state hypothesis. Site location - This study took place In The Las Cruces biological station Located in the southern Puntarenas province of Costa Rica during the months of June and July.. Sampling - Sampling was conducted with pitfall traps to reflect both population density and the mobility of the arthropods in a given habitat (McCary et al. 2014). Samples were collected, and pitfalls were recharged every five days. Samples were sorted and counted, and spiders and beetles’ taxonomic groups were further classified into families. We thank the National Science Foundation and the Louis Stokes Alliance for Minority Participation for financing this research project. Additionally, we thank Cuyahoga Community College for funding the presentation of this project at the SACNAS conference. This research was conducted under the Scientific Research Permit number: SINAC- ACLAP-146-2018. For more info please contact: [email protected] Anderson, S. J., & Death, R. G. (2000). The effect of forest type on forest floor invertebrate community structure. New Zealand Natural Sciences, 25, 33–41. Attwood, S. J., Maron, M., House, A. P., & Zammit, C. (2008). Do arthropod assemblages display globally consistent responses to intensified agricultural land use and management? Global Ecology and Biogeography, 585-599. Retrieved July 06, 2018. Cole, R. J., Holl, K. D., Zahawi, R. A., Wickey, P., & Townsend, A. R. (2016, May 12). Leaf litter arthropod responses to tropical forest restoration. Retrieved July 07, 2018. Culleney, T. W. (2013, September 25). Role of Arthropods in Maintaining Soil Fertility. Retrieved July 07, 2018. Dinnage, R., Cadotte, M. W., Haddad, N. M., Crutsinger, G. M., & Tilman, D. (2012). Diversity of plant evolutionary lineages promotes arthropod diversity. Ecology Letters. https://doi.org/10.1111/j.1461-0248.2012.01854.x Featured Creatures. 2018. U. (Ed.). (n.d.). Rove Beetles of Florida - Retrieved from http://entnemdept.ufl.edu/creatures/misc/beetles/fl_rove_beetles.htm#sele Hattenschwiler, S., Tiunov, A.V., & Scheu, S. (2005). Biodiversity and litter decomposition in terrestrial ecosystems. 191- 218. Hobbs, R., & Norton, D. (1996). Commentary Towards a Conceptual Framenwork for Restoration Ecology. Restoration Ecology, 93-110. Retrieved July 02, 2018. Arthropod Abundance per HabitatType Arthropods collected across the four habitat types (abandoned pasture M=445.5, secondary forest M=313, primary selectively-logged M=465.4 and primary forest M=609.8) totaled 14,622 individuals and were classified into four orders: Arachnida, Crustacea, Insecta, and Collembola. Total arthropod abundance was significantly higher in primary forest compared to the other forest types. Predatory Arthropod Abundance per Habitat Type Predatory arthropods were further identified and classified into 14 taxonomic groups. Additional test shows that total predatory arthropod abundance was not significantly different across forest types. INTRODUCTION MATERIALS AND METHODS DISCUSSION RESULTS ACKNOWLEDGMENTS REFERENCES Impact of Neotropical Wet Forest Restoration on the Predatory Arthropod Community in Southern Costa Rica Mónica J. Stevenson 1 and José-Cristian Martínez 2 1 Cuyahoga Community College, 11000 West Pleasant Valley Road, Parma, OH 44130, USA 2 Department of Biological Sciences, University of Illinois at Chicago, Chicago, IL 60607, USA

Transcript of Impact of Neotropical Wet Forest Restoration on the ... Stevenson SACNAS...presentation of this...

Page 1: Impact of Neotropical Wet Forest Restoration on the ... Stevenson SACNAS...presentation of this project at the SACNAS conference. This research was conducted under the Scientific Research

Arthropods are considered ecosystem engineers and are essential to the brown food web as they transform the soil by consuming plant debris and depositing feces that serve as food sources for micro-organisms, therefore, fostering microbial population growth and dispersal. This research aimed to assess how restoration stages affect arthropod populations and to validate the alternative state hypothesis.

Arthropod abundance was significantly higher in primary forest compared to other forests at different restoration stages:

• Evolutionary history of plant communities in this forest type favors arthropod population growth (Dinnage et al. 2012).

When focusing solely on the predatory arthropod community, the abundance difference across habitat type was not significant:

• Tree species diversity does not have an effect on predatory arthropod abundance (Vehvilainem et al. 2008).

These findings offer a useful foundation to better address ground-dwelling organisms in reforestation efforts in the Neotropics as they partially validate the alternative state hypothesis.

Site location - This study took placeIn The Las Cruces biological stationLocated in the southern Puntarenas province of Costa Rica during the months of June and July..

Sampling - Sampling was conducted with pitfall traps to reflect both population density and the mobility of the arthropods in a given habitat (McCary et al. 2014). Samples were collected, and pitfalls were recharged every five days. Samples were sorted and counted, and spiders and beetles’ taxonomic groups were further classified into families.

We thank the National Science Foundation and the Louis Stokes Alliance for Minority Participation for financing this research project. Additionally, we thank Cuyahoga Community College for funding the presentation of this project at the SACNAS conference. This research was conducted under the Scientific Research Permit number: SINAC-ACLAP-146-2018.

For more info please contact:[email protected]

Anderson, S. J., & Death, R. G. (2000). The effect of forest type on forest floor invertebrate community structure. New Zealand Natural Sciences, 25, 33–41.Attwood, S. J., Maron, M., House, A. P., & Zammit, C. (2008). Do arthropod assemblages display globally consistent responses to intensified agricultural land use and management? Global Ecology and Biogeography, 585-599. Retrieved July 06, 2018.Cole, R. J., Holl, K. D., Zahawi, R. A., Wickey, P., & Townsend, A. R. (2016, May 12). Leaf litter arthropod responses to tropical forest restoration. Retrieved July 07, 2018.Culleney, T. W. (2013, September 25). Role of Arthropods in Maintaining Soil Fertility. Retrieved July 07, 2018. Dinnage, R., Cadotte, M. W., Haddad, N. M., Crutsinger, G. M., & Tilman, D. (2012). Diversity of plant evolutionary lineages promotes arthropod diversity. Ecology Letters. https://doi.org/10.1111/j.1461-0248.2012.01854.xFeatured Creatures. 2018. U. (Ed.). (n.d.). Rove Beetles of Florida - Retrieved from http://entnemdept.ufl.edu/creatures/misc/beetles/fl_rove_beetles.htm#sele Hattenschwiler, S., Tiunov, A. V., & Scheu, S. (2005). Biodiversity and litter decomposition in terrestrial ecosystems. 191-218.Hobbs, R., & Norton, D. (1996). Commentary Towards a Conceptual Framenwork for Restoration Ecology. Restoration Ecology, 93-110. Retrieved July 02, 2018.

Arthropod Abundance per HabitatType

Arthropods collected across the four habitattypes (abandoned pasture M=445.5,secondary forest M=313, primaryselectively-logged M=465.4 and primaryforest M=609.8) totaled 14,622 individualsand were classified into four orders:Arachnida, Crustacea, Insecta, andCollembola.Total arthropod abundance was significantlyhigher in primary forest compared to theother forest types.

Predatory Arthropod Abundance per Habitat Type

Predatory arthropods were further identified and classified into 14 taxonomic groups. Additional test shows that total predatory arthropod abundance was not significantly different across forest types.

INTRODUCTION

MATERIALS AND METHODS

DISCUSSIONRESULTS

ACKNOWLEDGMENTS

REFERENCES

Impact of Neotropical Wet Forest Restoration on the Predatory Arthropod Community in Southern Costa Rica

Mónica J. Stevenson1 and José-Cristian Martínez21 Cuyahoga Community College, 11000 West Pleasant Valley Road, Parma, OH 44130, USA2 Department of Biological Sciences, University of Illinois at Chicago, Chicago, IL 60607, USA