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Effect of Reach-Level Changes in Ditch Morphology and Riparian Vegetation on Macroinvertebrate Communities in an Agricultural Landscape

Methods

General Design

  • Study reaches (150m long) selected a-priori

  • Control (n=6): No mature trees; bw/cw < 0.3

  • Bench (n=6): No mature trees; bw/cw > 0.5

  • Tree (n=7): Mature trees on both banks

Field Work

Benthic Community (sampled June 15 to July 15)

  • 6-10 Hess samples per reach

  • Each reach sampled one time in either 2001 or 2002

Morphology and Substrate (surveyed spring, summer or fall)

  • 2-4 cross-sections and longitudinal profile

  • Modified Wolman Pebble Count

  • Performed in either 2001 or 2002

Habitat Evaluation

Qualitative Habitat Evaluation Index (QHEI, Ohio EPA) completed for each site

Six category separations used:

  1. Substrate
  2. In-stream cover
  3. Channel morphology
  4. Riparian conditions
  5. Riffle/run development
  6. Pool/glide development

Laboratory Work

  • Separated macroinvertebrates from sample debris by visual inspection

  • Identified to lowest possible taxon (genus or species) and enumerated macroinvertebrates
    Exceptions:
    • Chironomidae (midges)
    • Oligochaeta (aquatic worms)
    • Hydracarina (water mites).

Computations and Data Analysis

  • Morphology Metrics
    • Bench development, water depths, channel gradient, wetted perimeter

  • Substrate Metrics
    • Texture class composition (relative %) of bed substrate
    • “Percent finer than” parameters (D16, D35, D50, D84, D95)

  • Macroinvertebrate Community Metrics
    • Taxa richness
    • Shannon diversity
    • Density
    • %EPT
    • Modified ICI
    • Rarefaction

  • ANOVA and nonparametrics (Kruskal-Wallis and Mann-Whitney) analyses used for group comparisons

  • Forward and backward stepwise linear regressions

 

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