Free Standard AU & NZ Shipping For All Book Orders Over $80!
Register      Login
The Rangeland Journal The Rangeland Journal Society
Journal of the Australian Rangeland Society
RESEARCH ARTICLE

Biosolids application increases grasshopper abundance in the short term in a northern Canadian grassland

Emma S. Gaudreault A , Robert G. Lalonde A , Kirstie Lawson A , Frank I. Doyle B and Karen E. Hodges A C
+ Author Affiliations
- Author Affiliations

A Department of Biology, University of British Columbia Okanagan, 1177 Research Road, Kelowna, BC. V1V 1V7, Canada.

B Wildlife Dynamics Consulting, 5575 Kleanza Drive, Terrace, BC. V8G 0A7, Canada.

C Corresponding author. Email: karen.hodges@ubc.ca

The Rangeland Journal 41(1) 55-64 https://doi.org/10.1071/RJ18075
Submitted: 28 July 2018  Accepted: 12 December 2018   Published: 24 January 2019

Abstract

Degraded grasslands are common worldwide, often due to overgrazing by livestock; such degradation often reduces plant growth and water quality, while increasing soil erosion, wildfires, and invasive species. Recent restoration efforts have used organic amendments to increase soil nutrients, improve water retention, and increase forage production. Biosolids, the stabilised and pathogen-treated remains from wastewater treatment plants, have strong impacts on soil nutrients and plant growth, but there is very little known about impacts on higher trophic levels. We worked on northern grasslands in British Columbia, Canada, to test whether biosolids applications changed grasshopper abundances, body sizes, or species richness. We used hoop transects to measure density and timed net samples to determine richness and evenness. There were significantly higher (~3.8×) grasshopper densities at sites where biosolids were applied 1–2 years before sampling compared with control sites or sites where biosolids were applied in the year of sampling. Tibia lengths of grasshoppers varied with treatment, species, and sex, but there was no clear signature of biosolids leading to bigger body sizes. There were no significant differences in species richness or equitability in relation to the year of the biosolids application. Collectively, our results show that biosolids have large impacts on grasshopper densities, but no clear impact on community structure or body size. Because grasshoppers can be dominant insect herbivores and are critical prey for many birds and mammals, our results suggest biosolids could be an important tool in the context of site restoration or efforts to improve populations of insectivorous vertebrates.

Additional keywords: abundance, biosolids, British Columbia, diversity, grasshoppers, grasslands.


References

Applebaum, S. W., and Heifetz, Y. (1999). Density-dependent physiological phase in insects. Annual Review of Entomology 44, 317–341.
Density-dependent physiological phase in insects.Crossref | GoogleScholarGoogle Scholar | 15012376PubMed |

Beckerman, A. P. (2000). Counterintuitive outcomes of interspecific competition between two grasshopper species along a resource gradient. Ecology 81, 948–957.
Counterintuitive outcomes of interspecific competition between two grasshopper species along a resource gradient.Crossref | GoogleScholarGoogle Scholar |

Belovsky, G. E., and Slade, J. B. (1995). Dynamics of two Montana grasshopper populations: relationships among weather, food abundance and intraspecific competition. Oecologia 101, 383–396.
Dynamics of two Montana grasshopper populations: relationships among weather, food abundance and intraspecific competition.Crossref | GoogleScholarGoogle Scholar | 28307061PubMed |

Branson, D. H., and Vermeire, L. T. (2016). Grasshopper responses to fire and postfire grazing in the Northern Great Plains vary among species. Rangeland Ecology and Management 69, 144–149.
Grasshopper responses to fire and postfire grazing in the Northern Great Plains vary among species.Crossref | GoogleScholarGoogle Scholar |

British Columbia Ministry of Agriculture (2015). Grasshopper Monitoring and Control in British Columbia. Available at: https://www2.gov.bc.ca/assets/gov/farming-natural-resources-and-industry/agriculture-and-seafood/animal-and-crops/plant-health/grasshopper-monitoring-and-control-in-bc.pdf (accessed 2 January 2019).

British Columbia Ministry of Environment (2015). Biosolids frequently asked questions and case studies. Available at: http://www.llbc.leg.bc.ca/public/pubdocs/bcdocs2015/588306/920f26452dd841f4b9f60bb4e2dc99ab.pdf

Brown, S., Chaney, R. L., Sprenger, M., and Compton, H. (2002). Assessing impact to wildlife at biosolids remediated sites. BioCycle 43, 50–58.

Canadian Council of Ministers of the Environment (2012). Canada-wide approach for the management of wastewater biosolids. PN 1477. Available at: https://www.ccme.ca/files/Resources/waste/biosolids/pn_1477_biosolids_cw_approach_e.pdf (accessed 2 January 2019).

Capinera, J., and Thompson, D. (1987). Dynamics and structure of grasshopper assemblages in shortgrass prairie. Canadian Entomologist 119, 567–575.
Dynamics and structure of grasshopper assemblages in shortgrass prairie.Crossref | GoogleScholarGoogle Scholar |

Capinera, J. L., Scott, R. D., and Walker, T. J. (2004). ‘Field Guide to Grasshoppers, Katydids, and Crickets of the United States.’ (Cornell University Press: Ithaca, NY.)

Cheng, C., Kimmins, J. P., and Sullivan, T. P. (1996). Forest fertilization with biosolids: impact on small mammal population dynamics. Northwest Science 70, 252–261.

Chisté, M. N., Mody, K., Gossner, M. M., Simons, N. K., Köhler, G., Weisser, W. W., and Blüthgen, N. (2016). Losers, winners, and opportunists: How grassland land-use intensity affects orthopteran communities. Ecosphere 7, e01545.
Losers, winners, and opportunists: How grassland land-use intensity affects orthopteran communities.Crossref | GoogleScholarGoogle Scholar |

Christodoulou, A., and Stamatelatou, K. (2016). Overview of legislation on sewage sludge management in developed countries worldwide. Water Science and Technology 73, 453–462.
Overview of legislation on sewage sludge management in developed countries worldwide.Crossref | GoogleScholarGoogle Scholar | 26877026PubMed |

Clarke, B. O., and Smith, S. R. (2011). Review of ‘emerging’ organic contaminants in biosolids and assessment of international research priorities for the agricultural use of biosolids. Environment International 37, 226–247.
Review of ‘emerging’ organic contaminants in biosolids and assessment of international research priorities for the agricultural use of biosolids.Crossref | GoogleScholarGoogle Scholar | 20797791PubMed |

Dyer, L. A., and Letourneau, D. (2003). Top-down and bottom-up diversity cascades in detrital vs. living food webs. Ecology Letters 6, 60–68.
Top-down and bottom-up diversity cascades in detrital vs. living food webs.Crossref | GoogleScholarGoogle Scholar |

Ebeling, A., Allan, E., Heimann, J., Köhler, G., Scherer-Lorenzen, M., Vogel, A., Weigelt, A., and Weisser, W. W. (2013). The impact of plant diversity and fertilization on fitness of a generalist grasshopper. Basic and Applied Ecology 14, 246–254.
The impact of plant diversity and fertilization on fitness of a generalist grasshopper.Crossref | GoogleScholarGoogle Scholar |

Elmhagen, B., and Rushton, S. P. (2007). Trophic control of mesopredators in terrestrial ecosystems: top-down or bottom-up? Ecology Letters 10, 197–206.
Trophic control of mesopredators in terrestrial ecosystems: top-down or bottom-up?Crossref | GoogleScholarGoogle Scholar | 17305803PubMed |

Fowler, A. C., Knight, R. L., George, T. L., and McEwen, L. C. (1991). Effects of avian predation on grasshopper populations in North Dakota grasslands. Ecology 72, 1775–1781.
Effects of avian predation on grasshopper populations in North Dakota grasslands.Crossref | GoogleScholarGoogle Scholar |

Fuchsman, P., Lyndall, J., Bock, M., Lauren, D., Barber, T., Leigh, K., Perruchon, E., and Capdeviellek, M. (2010). Terrestrial ecological risk evaluation for triclosan in land applied biosolids. Integrated Environmental Assessment and Management 6, 405–418.
Terrestrial ecological risk evaluation for triclosan in land applied biosolids.Crossref | GoogleScholarGoogle Scholar | 20821704PubMed |

Hartley, M. K., Rogers, W. E., Siemann, E., and Grace, J. (2007). Responses of prairie arthropod communities to fire and fertilizer: balancing plant and arthropod conservation. American Midland Naturalist 157, 92–105.
Responses of prairie arthropod communities to fire and fertilizer: balancing plant and arthropod conservation.Crossref | GoogleScholarGoogle Scholar |

Heidorn, T. J., and Joern, A. (1987). The feeding preference and spatial distribution of grasshoppers (Acrididae) in response to nitrogen fertilization of Calamovilfa longifolia. Functional Ecology 1, 369–375.
The feeding preference and spatial distribution of grasshoppers (Acrididae) in response to nitrogen fertilization of Calamovilfa longifolia.Crossref | GoogleScholarGoogle Scholar |

Joern, A., and Alward, R. (1988). Effect of nitrogen fertilization on choice among grasses by the grasshopper Phoetaliotes nebrascensis (Orthoptera: Acrididae). Annals of the Entomological Society of America 81, 240–244.
Effect of nitrogen fertilization on choice among grasses by the grasshopper Phoetaliotes nebrascensis (Orthoptera: Acrididae).Crossref | GoogleScholarGoogle Scholar |

Joern, A., and Behmer, S. T. (1998). Impact of diet quality on demographic attributes in adult grasshoppers and the nitrogen limitation hypothesis. Ecological Entomology 23, 174–184.
Impact of diet quality on demographic attributes in adult grasshoppers and the nitrogen limitation hypothesis.Crossref | GoogleScholarGoogle Scholar |

Johnson, D. L. (2008). Grasshopper identification and control methods: to protect crops and the environment. Agriculture and Agri-Foods Canada, Saskatoon, SK, Canada. 42 pp.

Krauss, J., Härri, S. A., Bush, L., Husi, R., Bigler, L., Pawer, S. A., and Müller, C. B. (2007). Effects of fertilizer, fungal endophytes and plant cultivar on the performance of insect herbivores and their natural enemies. Ecology 21, 107–116.

Krebs, C. J. (1998). ‘Ecological Methodology.’ 2nd edn. (Pearson: New York.)

Larney, F. J., and Angers, D. A. (2012). The role of organic amendments in soil reclamation: a review. Canadian Journal of Soil Science 92, 19–38.
The role of organic amendments in soil reclamation: a review.Crossref | GoogleScholarGoogle Scholar |

LeBauer, D. S., and Treseder, K. K. (2008). Nitrogen limitation of net primary productivity in terrestrial ecosystems is globally distributed. Ecology 89, 371–379.
Nitrogen limitation of net primary productivity in terrestrial ecosystems is globally distributed.Crossref | GoogleScholarGoogle Scholar | 18409427PubMed |

Lu, Q., He, Z. L., and Stoffella, P. J. (2012). Land application of biosolids in the USA: a review. Applied and Environmental Soil Science 2012, 201462.
Land application of biosolids in the USA: a review.Crossref | GoogleScholarGoogle Scholar |

McFarland, M. J., Vasquez, I. R., Vutran, M., Schmitz, M., and Brobst, R. B. (2010). Use of biosolids to enhance rangeland forage quality. Water Environment Research 82, 455–461.
Use of biosolids to enhance rangeland forage quality.Crossref | GoogleScholarGoogle Scholar | 20480767PubMed |

Monk, K. A. (1983). Morphological variation in relation to habitat in some British grasshoppers. Journal of Natural History 17, 75–85.
Morphological variation in relation to habitat in some British grasshoppers.Crossref | GoogleScholarGoogle Scholar |

Newman, R. F., Krzic, M., and Wallace, B. M. (2014). Differing effects of biosolids on native plants in grasslands of southern British Columbia. Journal of Environmental Quality 43, 1672–1678.
Differing effects of biosolids on native plants in grasslands of southern British Columbia.Crossref | GoogleScholarGoogle Scholar | 25603253PubMed |

O’Neill, K. M., and Rolston, M. G. (2007). Short-term dynamics of behavioral thermoregulation by adults of the grasshopper Melanoplus sanguinipes. Journal of Insect Science 7, 27.
Short-term dynamics of behavioral thermoregulation by adults of the grasshopper Melanoplus sanguinipes.Crossref | GoogleScholarGoogle Scholar |

Petrie, B., Barden, R., and Kasprzyk-Hordern, B. (2015). A review on emerging contaminants in wastewaters and the environment: Current knowledge, understudied areas and recommendations for future monitoring. Water Research 72, 3–27.
A review on emerging contaminants in wastewaters and the environment: Current knowledge, understudied areas and recommendations for future monitoring.Crossref | GoogleScholarGoogle Scholar | 25267363PubMed |

Randel, C. J., Aguirre, R. B., Peterson, M. J., and Silvy, N. J. (2006). Comparison of two techniques for assessing invertebrate availability for wild turkeys in Texas. Wildlife Society Bulletin 34, 853–855.
Comparison of two techniques for assessing invertebrate availability for wild turkeys in Texas.Crossref | GoogleScholarGoogle Scholar |

Ritchie, M. E., and Tilman, D. (1993). Predictions of species interactions from consumer-resource theory: experimental tests with grasshoppers and plants. Oecologia 94, 516–527.
Predictions of species interactions from consumer-resource theory: experimental tests with grasshoppers and plants.Crossref | GoogleScholarGoogle Scholar | 28313992PubMed |

Rosenberg, D. M., Danks, H. V., and Lehmkuhl, D. M. (1986). Importance of insects in environmental impact assessment. Environmental Management 10, 773–783.
Importance of insects in environmental impact assessment.Crossref | GoogleScholarGoogle Scholar |

San Martin y Gomez, G., and Van Dyck, H. (2012). Ecotypic differentiation between urban and rural populations of the grasshopper Chorthippus brunneus relative to climate and habitat fragmentation. Oecologia 169, 125–133.
Ecotypic differentiation between urban and rural populations of the grasshopper Chorthippus brunneus relative to climate and habitat fragmentation.Crossref | GoogleScholarGoogle Scholar | 22108853PubMed |

Sharma, B., Sarkar, A., Singh, P., and Singh, R. P. (2017). Agricultural utilization of biosolids: A review on potential effects on soil and plant grown. Waste Management 64, 117–132.
Agricultural utilization of biosolids: A review on potential effects on soil and plant grown.Crossref | GoogleScholarGoogle Scholar | 28336334PubMed |

SYLVIS (2008). Land application guidelines for organic matter recycling regulation and the soil amendment code of practice – Best management practices. Prepared for British Columbia Ministry of Environment.

United States Department of Agriculture (USDA) (2014). Grasshoppers of the western US. Available at: http://idtools.org/id/grasshoppers/factsheet_index.php (accessed 2 January 2019).

Unsicker, S. B., Franzke, A., Specht, J., Hohler, G., and Linz, J. (2010). Plant species richness in montane grasslands affects the fitness of a generalist grasshopper species. Ecology 91, 1083–1091.
Plant species richness in montane grasslands affects the fitness of a generalist grasshopper species.Crossref | GoogleScholarGoogle Scholar | 20462122PubMed |

Wallace, B. M., Krzic, M., Newman, R. F., Forge, T. A., Broersma, K., and Neilsen, G. (2016). Soil aggregate dynamics and plant community response after biosolids application in a semiarid grassland. Journal of Environmental Quality 45, 1663–1671.
Soil aggregate dynamics and plant community response after biosolids application in a semiarid grassland.Crossref | GoogleScholarGoogle Scholar | 27695737PubMed |

Washburn, B. E., and Begier, M. (2011). Wildlife responses to long-term application of biosolids to grasslands in North Carolina. Rangeland Ecology and Management 64, 131–138.

Zhang, M., and Fielding, D. J. (2011). Populations of the northern grasshopper, Melanoplus borealis (Orthoptera: Acrididiae), in Alaska are rarely food limited. Environmental Entomology 40, 541–548.
Populations of the northern grasshopper, Melanoplus borealis (Orthoptera: Acrididiae), in Alaska are rarely food limited.Crossref | GoogleScholarGoogle Scholar | 22251631PubMed |