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Comparison of Stream Invertebrate Response Models for Bioassessment Metrics1
Authors:Ian R Waite  Jonathan G Kennen  Jason T May  Larry R Brown  Thomas F Cuffney  Kimberly A Jones  James L Orlando
Institution:1. Respectively, Biologist (Waite), U.S. Geological Survey, Oregon Water Science Center, 2130 SW 5th Avenue, Portland, Oregon 97201;2. Biologist (Kennen), U.S. Geological Survey, New Jersey Water Science Center, Trenton, New Jersey 08628;3. Biologist (May and Brown) and Hydrologist (Orlando), U.S. Geological Survey, California Water Science Center, Sacramento, California 95819;4. Biologist (Cuffney), U.S. Geological Survey, North Carolina Water Science Center, Raleigh, North Carolina 27607;5. Physical Scientist (Jones), U.S. Geological Survey, Utah Water Science Center, West Valley, Utah 84119
Abstract:Waite, Ian R., Jonathan G. Kennen, Jason T. May, Larry R. Brown, Thomas F. Cuffney, Kimberly A. Jones, and James L. Orlando, 2012. Comparison of Stream Invertebrate Response Models for Bioassessment Metrics. Journal of the American Water Resources Association (JAWRA) 48(3): 570-583. DOI: 10.1111/j.1752-1688.2011.00632.x Abstract: We aggregated invertebrate data from various sources to assemble data for modeling in two ecoregions in Oregon and one in California. Our goal was to compare the performance of models developed using multiple linear regression (MLR) techniques with models developed using three relatively new techniques: classification and regression trees (CART), random forest (RF), and boosted regression trees (BRT). We used tolerance of taxa based on richness (RICHTOL) and ratio of observed to expected taxa (O/E) as response variables and land use/land cover as explanatory variables. Responses were generally linear; therefore, there was little improvement to the MLR models when compared to models using CART and RF. In general, the four modeling techniques (MLR, CART, RF, and BRT) consistently selected the same primary explanatory variables for each region. However, results from the BRT models showed significant improvement over the MLR models for each region; increases in R2 from 0.09 to 0.20. The O/E metric that was derived from models specifically calibrated for Oregon consistently had lower R2 values than RICHTOL for the two regions tested. Modeled O/E R2 values were between 0.06 and 0.10 lower for each of the four modeling methods applied in the Willamette Valley and were between 0.19 and 0.36 points lower for the Blue Mountains. As a result, BRT models may indeed represent a good alternative to MLR for modeling species distribution relative to environmental variables.
Keywords:modeling  macroinvertebrates  watershed disturbance  land use  prediction  statistical assessment
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