Biological assessment of freshwater ecosystems using a reference condition approach: comparing predicted and actual benthic invertebrate communities in Yukon streams

1. The reference condition approach to bioassessment is based on comparing a biological community found at a test site to the range of communities observed at a set of reference sites. A community descriptor (e.g. number of taxa) is estimated for the test site. If the value of the descriptor falls outside of a given boundary, or biocriterion, from the distribution of the descriptors for the reference sites, the test site fails. 2. The sensitivity of the reference condition approach can be increased by modelling and explaining variation in the community descriptor among the reference sites, and then using the predictive model to refine the expectation of the descriptor’s value at a test site. 3. This study applied the reference condition approach, with predictive modelling, to the bioassessment, using benthic macroinvertebrate (BMI) communities, of streams exposed to placer gold mining effluent in central Yukon Territory, Canada. The major changes to the stream caused by mining are increased turbidity and metal concentrations. 4. Among reference sites sampled from 1993 to 1995, a predictive model using year of sampling and simple geographical characteristics (distance to source of the stream, upstream catchment area, altitude, two-way interactions) explained over half of the variation in each of five BMI community descriptors including richness (number of families), Simpson’s diversity, Simpson’s equitability, family biotic index and Bray–Curtis distance to the median reference community. 5. Biocriteria (other than Bray–Curtis distance to the median community) based on the predictive models failed a far greater proportion of sites currently exposed to placer mining (50–100%) than biocriteria not based on predictive models (7–71%). A similar increase in the sensitivity of the bioassessment was seen when evaluating sites previously exposed to placer mining effluent. The simplest, most sensitive bioassessment of the effects of placer gold mining effluent on stream ecosystems used richness (number of families) of the BMI community together with a predictive model.

[1]  Robert C. Bailey,et al.  Biological guidelines for freshwater sediment based on BEnthic Assessment of SedimenT (the BEAST) using a multivariate approach for predicting biological state , 1995 .

[2]  R. Bailey,et al.  An Inexpensive Stream Bottom Sampler , 1981 .

[3]  J. Gerritsen,et al.  Additive Biological Indices for Resource Management , 1995, Journal of the North American Benthological Society.

[4]  R. Hopcroft,et al.  High precision microcomputer based measuring system for ecological research , 1986 .

[5]  Richard H. Norris,et al.  Biological Monitoring: The Dilemma of Data Analysis , 1995, Journal of the North American Benthological Society.

[6]  R. Bailey,et al.  Does taxonomic resolution affect the multivariate description of the structure of freshwater benthic macroinvertebrate communities , 1997 .

[7]  Wayne S. Davis,et al.  Biological assessment and criteria : tools for water resource planning and decision making , 1995 .

[8]  S. Ormerod,et al.  The constancy of invertebrate assemblages in soft-water streams : implications for the prediction and detection of environmental change , 1990 .

[9]  L. Corkum Patterns of benthic invertebrate assemblages in rivers of northwestern North America , 1989 .

[10]  K. Cummins,et al.  An Introduction to the Aquatic Insects of North America , 1981 .

[11]  James R. Karr,et al.  Regional Application of an Index of Biotic Integrity Based on Stream Fish Communities , 1984 .

[12]  Mike T. Furse,et al.  A preliminary classification of running‐water sites in Great Britain based on macro‐invertebrate species and the prediction of community type using environmental data , 1984 .

[13]  D. Barton The use of Percent Model Affinity to assess the effects of agriculture on benthic invertebrate communities in headwater streams of southern Ontario, Canada , 1996 .

[14]  W. Hilsenhoff Rapid Field Assessment of Organic Pollution with a Family-Level Biotic Index , 1988, Journal of the North American Benthological Society.

[15]  J. B. Reynolds,et al.  EFFECTS OF PLACER MINING DISCHARGE ON HEALTH AND FOOD OF ARCTIC GRAYLING1 , 1989 .

[16]  E. V. Nieuwenhuyse,et al.  EFFECTS OF PLACER GOLD MINING ON PRIMARY PRODUCTION IN SUBARCTIC STREAMS OF ALASKA , 1986 .

[17]  Mike T. Furse,et al.  The prediction of the macro‐invertebrate fauna of unpolluted running‐water sites in Great Britain using environmental data , 1987 .

[18]  R. W. Bode,et al.  Percent Model Affinity: A New Measure of Macroinvertebrate Community Composition , 1992, Journal of the North American Benthological Society.

[19]  Stephen M. Wagener,et al.  Effects of Placer Mining on the Invertebrate Communities of Interior Alaska Streams , 1985, Freshwater Invertebrate Biology.