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![Page 1: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/1.jpg)
Stream macroinvertebrate responses to landscape variables; an evaluation
of rapid bioassessment techniques using a statistical modeling approach.
• Declan J. McCabe1 and Philip A. Yates2
1. Saint Michael’s College Biology 2. Saint Michael’s College Mathematics
![Page 2: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/2.jpg)
Acknowledgements
• This work could not have been done without the help of Kaitlyn Berry; Alex Canepa; Tyler Gillingham; Erin Hayes-Pontius; Bridget Levine; Lexie Haselton
• Work made possible by funding from Vermont EPSCoR with additional support from Saint Michael’s College
![Page 3: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/3.jpg)
Stream Macroinvertebrate biomonitoring at Saint Michael’s
College• Ongoing since 2008
• 60+ site database
• Modeling watershed effects on invertebrate communities
• Our focus today – 53 sites; modeling project
![Page 4: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/4.jpg)
Sampling• Each stream:
• 4 kick net samples
• Identification by trained interns
• Standard keys
• Iphone app
![Page 5: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/5.jpg)
• Primary research questions• Intern presentations (ASLO; LCRC; SACNAS etc.)• High school outreach support
Samples serve many purposes
![Page 6: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/6.jpg)
Landscape data• GIS-derived watershed
characterization• Reclassified 2006 C-CAP (Costal
Change Analysis Program) land coverage data
• Macroinvertebrate samples from 2008 through 2010 used to characterize streams along an urban/forested gradient
![Page 7: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/7.jpg)
Landscape parametersCatchment Area AcresAgricultural AcresPercent Catchment AgriculturalUrban AcresPercent Catchment UrbanForested AcresPercent Catchment ForestedUpstream Distance Lake Pond (m)Upstream Distance Dam (m)Upstream Distance Bridge (m)Upstream Distance Culvert (m)Distance To Tributary Mouth (m)Percent Catchment Highly Erodible SoilsStream Order
E911 Structure CountE911 Structures per AcreE911 New 2008Stream Gradient for 100m Stream SegmentAspect for 100m Stream Segment BufferSinuosityDominant Bedrock ClassAverage Catchment Area Elevation (m)Monitoring Site Elevation (ft)Length Road Network in Catchment (km)Length Road Network in Catchment (m)Length Road Network Gravel (km)Length Road Network Gravel (m)
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Parameters in our generalized additive models
• Catchment Area Acres• Forest principal component• Agricultural component• Upstream Distance Lake Pond (m)• Upstream Distance Dam (m)• Upstream Distance Bridge (m)• Upstream Distance Culvert (m)• Distance to Tributary Mouth (m)• Stream Gradient for 100m Stream Segment• Aspect for 100m Stream Segment Buffer• Sinuosity• Dominant Bedrock Class
![Page 9: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/9.jpg)
Macroinvertebrate responses• EPA’s 14 candidate
benthic metrics for measuring effects of perturbation (Barbour et al 1999):
• Vermont Departmental of Environmental Conservation biocriteria (2004)
• Merritt, Cummins, and Berg (2008)
Richness measures Total No. taxa No. EPT taxa
No. Ephemeroptera Taxa No. Plecoptera Taxa No. Trichoptera Taxa
Composition measures % EPT
% Ephemeroptera No. of Intolerant Taxa
Tolerance/Intolerance measures % Tolerant Organisms
% Dominant TaxonFeeding measures
% Filterers % Grazers and Scrapers
Habit measures Number of Clinger Taxa
% Clingers
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Model details• Principal components
analysis used to generate a landscape axis that best explained each macroinvertebrate response variable
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Model details• GIS data used to predict occurrence of each
species along the PCA axis based on a binary distribution
• The predicted species present data are summed to yield a predicted community
• Standard metrics can be measured from the predicted community and compared to observed
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Example
9.00 20.00 31.00 42.009.00
20.00
31.00
42.00
Taxonomic richness
95% confidence limit
Predicted taxonomic richness
Obs
erve
d ta
xono
mic
rich
ness
![Page 13: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/13.jpg)
Which index best responds?• Metrics yielding models with the tightest fit:– % filterers; % Ephemeroptera; % grazers; % clingers
• Metrics specifically responding to land use:– Forested land increased % EPT & % Ephemeroptera– Agricultural land increases % filterers & % clingers
• Metrics that could not be modeled:– Plecoptera richness; Trichoptera richness; # of
intolerant taxa
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What landscape parameters were most influential?
• We ranked the factors influencing each response variable; Example:
![Page 15: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/15.jpg)
What landscape parameters were most influential?
We summed the ranks to find the characteristics that had the largest influence on the most benthic metrics:
![Page 16: Stream macroinvertebrate responses to landscape variables; an evaluation of rapid bioassessment techniques using a statistical modeling approach. Declan.](https://reader035.fdocuments.in/reader035/viewer/2022070403/56649f2a5503460f94c44eaf/html5/thumbnails/16.jpg)
Next steps
• Test the models using 6 new sites ranging in land use
Questions?