Macroinvertebrate community response to natural and forest harvest gradients in western Oregon headwater streams

Summary 1. To examine the effects of forest harvest practices on headwater stream macroinvertebrates, we compiled a 167 site database with macroinvertebrate, fish, physical habitat and catchment land cover data from the three forested ecoregions in western Oregon. For our analysis, headwater streams were defined by catchment areas <10 km2 and perennial water during summer low flows. Almost all sites in the database were selected using a randomised survey design, constituting a representative sample of headwater streams in these ecoregions. 2. Macroinvertebrate taxonomic and functional feeding group composition were very similar among the three ecoregions in the study area (Coast Range, Cascades and Klamath Mountains). On average, 55% of the individuals at each site were in the orders Ephemeroptera, Plecoptera or Trichoptera. Dipteran taxa (mostly chironomids) accounted for another 34%. At almost all sites, non-insects made up <10% of the macroinvertebrate assemblage. Almost half (49%) of the assemblages were collectors; remaining individuals were about evenly divided among scrapers, shredders and predators. 3. There were 189 different macroinvertebrate taxa at the 167 sites with richness at individual sites ranging from 7 to 71 taxa. Ordination by non-metric multidimensional scaling revealed a strong association between % Ephemeroptera, especially Baetis, and site scores along the first axis. This axis was also strongly related to % coarse substratum and fast water habitat. The second axis was strongly related to % intolerant individuals, site slope and altitude. No strong relationships were evident between any ordination axis and either logging activity, presence/absence of fish, catchment size or ecoregion. 4. Based on macroinvertebrate index of biotic integrity (IBI) scores, 62% of the sites had no impairment, 31% of the sites had slight impairment and only 6% of the sites had moderate or severe impairment. IBI scores were not strongly related to forest harvest history. All four severely impaired sites and five of the seven sites with moderate impairment were lower altitude, shallower slope stream reaches located in the Coast Range with evidence of agricultural activity in their catchment or riparian zone. % sand + fine substratum was the environmental variable most strongly related to macroinvertebrate IBI.

[1]  C. Federer,et al.  Effects of forest clearcutting in New England on stream macroinvertebrates and periphyton , 1986 .

[2]  Henry A. Froehlich,et al.  Woody debris, channel features, and macroinvertebrates of streams with logged and undisturbed riparian timber in northeastern Oregon, U.S.A. , 1990 .

[3]  Richard H. Norris,et al.  DEVELOPMENT AND EVALUATION OF PREDICTIVE MODELS FOR MEASURING THE BIOLOGICAL INTEGRITY OF STREAMS , 2000 .

[4]  Steven G. Paulsen,et al.  Designing a Spatially Balanced, Randomized Site Selection Process for Regional Stream Surveys: The EMAP Mid-Atlantic Pilot Study , 2000 .

[5]  R. Marchant,et al.  Do rare species have any place in multivariate analysis for bioassessment? , 2002, Journal of the North American Benthological Society.

[6]  B. Harvey Benthic assemblages in Utah headwater streams with and without trout , 1993 .

[7]  David P. Larsen,et al.  Comparing strengths of geographic and nongeographic classifications of stream benthic macroinvertebrates in the Mid-Atlantic Highlands, USA , 2000, Journal of the North American Benthological Society.

[8]  David R. Barton,et al.  Dimensions of Riparian Buffer Strips Required to Maintain Trout Habitat in Southern Ontario Streams , 1985 .

[9]  A. Magurran Ecological Diversity and Its Measurement , 1988, Springer Netherlands.

[10]  B. Cosby,et al.  Effects of Climate Events on Elemental Fluxes from Forested Catchments in Ontario, Canada: Modelling Drought-Induced Redox Processes , 2004 .

[11]  R. Sidle,et al.  Understanding Processes and Downstream Linkages of Headwater Systems , 2002 .

[12]  R. H. Myers Classical and modern regression with applications , 1986 .

[13]  Frederick J. Swanson,et al.  Flood Disturbance in a Forested Mountain Landscape Interactions of land use and floods , 1998 .

[14]  M. L. Murphy,et al.  Effects of canopy modification and accumulated sediment on stream communities. , 1981 .

[15]  J. Stoddard,et al.  Development and Evaluation of a Macroinvertebrate Biotic Integrity Index (MBII) for Regionally Assessing Mid-Atlantic Highlands Streams , 2003, Environmental management.

[16]  W. Cohen,et al.  Characterizing 23 Years (1972–95) of Stand Replacement Disturbance in Western Oregon Forests with Landsat Imagery , 2002, Ecosystems.

[17]  Charles P. Hawkins,et al.  Evaluation of the use of landscape classifications for the prediction of freshwater biota: synthesis and recommendations , 2000, Journal of the North American Benthological Society.

[18]  C. Seeliger,et al.  Quantifying physical habitat in wadeable streams : surface waters , 1999 .

[19]  Robert M. Hughes,et al.  Classification strengths of ecoregions, catchments, and geographic clusters for aquatic vertebrates in Oregon , 2000, Journal of the North American Benthological Society.

[20]  J. Hutchens,et al.  Bioassessment of silvicultural impacts in streams and wetlands of the Eastern United States , 2004 .

[21]  John Van Sickle,et al.  Using Mean Similarity Dendrograms to Evaluate Classifications , 1997 .

[22]  Charles P. Hawkins,et al.  Weak correspondence between landscape classifications and stream invertebrate assemblages: implications for bioassessment , 2000, Journal of the North American Benthological Society.

[23]  W. Hilsenhoff,et al.  An Improved Biotic Index of Organic Stream Pollution , 2017, The Great Lakes Entomologist.

[24]  J. Feminella Correspondence between stream macroinvertebrate assemblages and 4 ecoregions of the southeastern USA , 2000, Journal of the North American Benthological Society.

[25]  Correspondence of stream benthic invertebrate assemblages to regional classification schemes in Missouri , 2000, Journal of the North American Benthological Society.

[26]  Todd J. Mabee,et al.  Relation of headwater macroinvertebrate communities to in-stream and adjacent stand characteristics in managed second-growth forests of the Oregon Coast Range mountains 1 , 2003 .

[27]  J. Omernik Ecoregions of the Conterminous United States , 1987 .

[28]  L. Williams,et al.  Large-Scale Effects of Timber Harvesting on Stream Systems in the Ouachita Mountains, Arkansas, USA , 2002, Environmental management.

[29]  Arthur V. Brown,et al.  Responses of benthic macroinvertebrates in small intermittent streams to silvicultural practices , 1997, Hydrobiologia.

[30]  R. Sidle,et al.  The characteristics of woody debris and sediment distribution in headwater streams, southeastern Alaska , 2001 .

[31]  M. Brusven,et al.  Effects of Canopy Removal on Invertebrates and Diet of Juvenile Coho Salmon in a Small Stream in Southeast Alaska , 1998 .

[32]  L. A. Smock,et al.  Effects of logging on macroinvertebrate production in a sand‐bottomed, low‐gradient stream , 2001 .

[33]  J. D. Newbold,et al.  Effects of Logging on Macroinvertebrates in Streams With and Without Buffer Strips , 1980 .

[34]  M. L. Murphy,et al.  Effects of Canopy, Substrate Composition, and Gradient on the Structure of Macroinvertebrate Communities in Cascade Range Streams of Oregon , 1982 .

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

[36]  Bruce McCune,et al.  Improving community analysis with the Beals smoothing function , 1994 .

[37]  Limin Yang,et al.  COMPLETION OF THE 1990S NATIONAL LAND COVER DATA SET FOR THE CONTERMINOUS UNITED STATES FROM LANDSAT THEMATIC MAPPER DATA AND ANCILLARY DATA SOURCES , 2001 .

[38]  W. P. Williams,et al.  Measuring the responses of macroinvertebrate communities to water pollution: a comparison of multivariate approaches, biotic and diversity indices , 2004, Hydrobiologia.

[39]  J. Stockner,et al.  Autotrophic Production in Carnation Creek, a Coastal Rainforest Stream on Vancouver Island, British Columbia , 1976 .

[40]  J. B. Wallace,et al.  Long‐term recovery of a mountain stream from clear‐cut logging: the effects of forest succession on benthic invertebrate community structure , 1998 .