Brome ( Bromus inermis ) in Fescue Grasslands at Riding Mountain - - PowerPoint PPT Presentation

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Brome ( Bromus inermis ) in Fescue Grasslands at Riding Mountain - - PowerPoint PPT Presentation

Soil Properties in Relation to Smooth Brome ( Bromus inermis ) in Fescue Grasslands at Riding Mountain National Park Colleen Robertson Department of Environment and Geography, University of Manitoba, Winnipeg, Manitoba


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Soil Properties in Relation to Smooth Brome (Bromus inermis) in Fescue Grasslands at Riding Mountain National Park

Colleen Robertson

Department of Environment and Geography, University of Manitoba, Winnipeg, Manitoba

robertsoncolleen11@gmail.com

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SLIDE 2

Objectives

  • Understand the differential invasion of smooth

brome as it spreads from the initial point of introduction

  • Understand the impact smooth brome stands

have on soil properties

  • Consider geophysical imaging as a tool in

smooth brome monitoring and management

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SLIDE 3

Background

  • Smooth brome threatens ecological integrity of

grassland ecosystems (Otfinowski et al., 2007)

  • Initially introduced via roads and trails, spreads

differentially into surrounding ecosystems (Gifford and

Otfinowski, 2013)

  • Stands decrease in density over time—depletion of

nutrients (Otfinowski et al., 2007)

  • Roots are dense and extend deep into soil (Piper et al.,

2015)

  • Higher moisture requirement than many

grassland plants (Stotz et al., 2016)

 If water is limited, will grow where soil moisture is highest

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SLIDE 4

Hypotheses

  • 1. Smooth brome will be present where

higher moisture content is available and where soils are acidic

  • 2. Plant nutrients will be depleted where

smooth brome is present

  • 3. Soil will have a higher proportion of
  • rganic carbon where smooth brome is

present

  • 4. Water availability will be a more

important factor in the xeric prairie than the mesic prairie

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SLIDE 5

Location and Site Selection

  • Data collected July-August 2019 in

Riding Mountain National Park, Manitoba

  • Study focused on Grasshopper

Valley and Peden Prairie

 Geographically separated  Differing moisture content

  • 5 hectare area defined for study in

each grassland

Grasshopper Valley Peden Prairie

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Soil Sampling

Grasshopper Valley Peden Prairie 0-15cm 15-30cm 30-45cm 45-60cm

Many roots Very few roots

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Soil Sampling and Laboratory Analyses

  • Litter depth and surface volumetric

moisture also sampled at each site

  • Soil samples analyzed for:

 pH  EC  Available phosphorus  Available nitrogen  Total Nitrogen  Total Carbon  Total Organic Carbon  C:N ratio

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SLIDE 8

Geophysical Imaging

  • Geonics EM-38 survey for ground

conductance

 Uses EMI to measure apparent electrical conductance  Influenced by moisture, texture, salinity

  • Digital elevation model generated by

differential GPS

  • Drone imaging for NDVI and NDRE indices

https://grdc.com.au/resources-and-publications/grdc-update-papers/tab-content/grdc-update- papers/2013/03/a-how-to-for-getting-soil-water-from-your-em38-field-measurements

Foley, 2013

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SLIDE 9

Results: Soil Chemistry

  • Smooth brome presence impacts

TOC and inorganic nitrogen

  • Grasshopper Valley:

 Smooth brome not effecting soil properties in the 45-60cm range (no difference in TOC)  Significant difference in pH and available phosphorus in the 45- 60cm range

Site Depth Brome PO4-P

(mg/kg)

pH NH4-N

(mg/kg)

NO3-N

(mg/kg)

TOC (%) present 8.51 6.5 9.3 0.3 8.00 absent 9.28 6.8 11.7 1.0 7.17 present 4.16 6.8 5.4 4.69 absent 3.90 7.3 5.1 3.88 present 2.82 7.1 3.6 2.99 absent 3.87 8.0 4.2 2.42 present 3.24 7.3 3.6 0.127 absent 4.61 8.0 4.2 0.207 present 8.59 6.5 7.1 1.8 8.70 absent 11.09 6.1 10 1.4 8.80 present 4.5 6.7 5.6 5.49 absent 2.41 6.4 5.2 3.70 present 2.88 7.3 4.1 3.22 absent 1.64 7.1 3.4 2.44 present 4.12 7.7 4.7 3.21 absent 2.91 7.4 3.9 2.73

45-60cm

Peden Prairie

0-15cm 15-30cm 30-45cm 30-45cm

Grasshopper Valley

0-15cm 15-30cm 45-60cm

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SLIDE 10

Digital Elevation Model Ground Conductance Model

Results: Geophysical Imaging

Normalized Difference Red-Edge Normalized Difference Vegetation Index

Indicates significant difference between brome-presence and brome-absence

Grasshopper Valley (mesic grassland)

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Digital Elevation Model Ground Conductance Model

Results: Geophysical Imaging

Normalized Difference Red-Edge Normalized Difference Vegetation Index

Indicates significant difference between brome-presence and brome-absence

Peden Prairie (xeric grassland)

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Results: Water Availability

  • Grasshopper Valley (mesic):

 Ground conductance significantly higher in brome-presence  High ground conductance indicating higher soil moisture

  • Peden Prairie (xeric):

 Elevation significantly lower in brome-presence  Brome is establishing in depressions- higher soil moisture

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Influence of Soil Properties on Smooth Brome Invasion

  • Grasshopper Valley

 Negligible impact from brome presence in 45-60cm depth (No difference in TOC)  45-60cm depth represents pre-invasion soil condition  Invasion influenced by acidic soils, low available phosphorus, and high ground conductance

  • Peden Prairie

 Mostly dictated by proximity to the trail  Depressed elevation

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Geophysical Imaging in Smooth Brome Management

  • Small scale conductance and elevation

changes can be used to create a model of invasion susceptibility

 Next steps: improve resolution of models, minimize disturbance to grassland

  • NDRE has potential to be used to map smooth

brome foci over large areas

  • Further research needed to refine models
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SLIDE 15

Conclusion

  • Factors determining invasion risk

depend on the moisture content of the grassland

 Peden Prairie (Moisture limiting): low elevation (soil moisture)  Grasshopper Valley (Moisture not limiting): acidic soils, low available phosphorus, high ground conductance (soil moisture)

  • Geophysical imaging has the potential

to enhance monitoring and management practices of smooth brome and other invasive species

 Research to refine models is needed for the effective use of imaging techniques

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References

Gifford, M., & Otfinowski, R. (2013). Landscape Disturbances Impact Affect the Distribution and Abundance of Exotic Grasses in Northern Fescue Prairies, 577–584. Otfinowski, R., Kenkel, N. C., & Catling, P. M. (2007). The biology of Canadian weeds. 134. Bromus inermis Leyss, 2(1982): 54–56. Piper, C.L., Sicilano, S.D., Winsley, T, Lamb, E.G. (2015) Smooth brome invasion increases rare soil bacteria species prevalence, bacterial species richness and evenness. Journal of Ecology. 103: 386-396. Stotz, G., Dettlaff, M., Pec, G., Inderjit, Carrigy, A., Stotz, G., … Cahill, J. (2016). Community-level determinants of smooth brome (Bromus inermis) growth and survival in the aspen parkland. Plant Ecology, 217(11), 1395–1413.

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Questions?

Thank you:

Mario Tenuta and Peter Tarleton for your guidance Mervin Bilous, Matt Gervais, and Krista Hanis-Gervais from the U of M ASEL John Fitzmaurice, Matthew Friesen and Mike Chubey from Agriculture and Agri- food Canada Roxanne Grzela, Roberta Tesar, Skye Rees, Kathryn Yarchuk, Sean Frey, Melanie Robinson and others from the Riding Mountain National Park resource conservation team Norman Kenkel and Cole Stocki for assistance with analyses