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Defining Least-Impacted Reference Condition for the National Wadeable Streams Assessment

Defining Least-Impacted Reference Condition for the National Wadeable Streams Assessment. Alan Herlihy (Oregon State University), John Stoddard (U.S. EPA, NHEERL-WED), Chuck Hawkins (Utah State University), and Susan Holdsworth (U.S. EPA, OW).

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Defining Least-Impacted Reference Condition for the National Wadeable Streams Assessment

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  1. Defining Least-Impacted Reference Condition for the National Wadeable Streams Assessment Alan Herlihy (Oregon State University), John Stoddard (U.S. EPA, NHEERL-WED), Chuck Hawkins (Utah State University), and Susan Holdsworth (U.S. EPA, OW)

  2. Why do we want to select and sample reference streams? • Are necessary for the interpretation of national monitoring data • Provide benchmark for evaluation of ecological condition (e.g. biotic integrity)

  3. What is Reference Condition? • Minimally Disturbed Condition – site condition in the absence of significant human disturbance (e.g., “natural,” “pristine” or “undisturbed”) • Least Disturbed Condition –found in conjunction with the best available physical, chemical and biological habitat conditions given today’s state of the landscape - defined by a set of explicit criteria to which all reference sites must adhere

  4. How are reference sites chosen? Often chosen by best professional judgment (BPJ) BPJ sites have varying and unknown quality Alternative: Filter survey data for physical-chemical stressors to identify best sites

  5. Mid-Atlantic Highlands EMAP Stream Example • Screen all sites and remove those with: • Sulfate > 400 µeq/L (~20 mg/L) • Acid Neutralizing Capacity (ANC)< 50µeq/L (~ 2.5 mg/L CaCO3 or pH ~6) • Total phosphorus > 20 µg/L • Total nitrogen > 750 µg/L • Chloride > 100 µeq/L (~3.5 mg/L) • Mean RBP habitat score < 15

  6. Expected stream sulfate from deposition in this region is 100-300 µeq/L • Bimodal sulfate histogram in Plateau. Mining not common in Ridge & Valley (except for Anthracite Belt) • Sites with SO4>400 µeq/L classified as non-reference

  7. Contrary Creek, VirginiapH=3, SO4=5,000 µeq/L

  8. Montgomery Creek, PApH=5.1, SO4=175 µeq/L

  9. Filtering produced a set of Reference Sites with higher EPT Richness scores than BPJ • Advantages of Filtered Sites • Fewer poor biological condition sites • Have a much more rigorous definition of “reference”

  10. EMAP-West Summer 2000-2004 12 Western States 841 Probability Sites Hand-Picked Sites sampled by EMAP protocols State BPJ Sites Corvallis GIS/Field Screen STAR Grant Ref Sites WSA Summer 2004 36 Eastern & Central States 541 Probability Sites Hand-Picked Sites Sampled by EMAP Protocols State BPJ Sites Wadeable Stream Assessment Sample

  11. WEMAP Filtered all sites collected with EMAP protocols Probability, BPJ, GIS Four Approaches - Delphi STAR Grant Sites Pristine Good Low Dropped in MT ecoregions WSA Filtered all sites collected with EMAP protocols Probability, BPJ Needed more reference sites, augmented with existing, State Data NAWQA data Earlier Filtered EMAP and REMAP data Reference Site Data for Assessment

  12. 9 Aggregate Level III Ecoregions used to set filtering criteria

  13. WSA Reference Exclusion Criteria

  14. Filtered Filtered

  15. Filtered

  16. Filtered Filtered

  17. Number of Reference Sites Used in WSA

  18. Number of Reference Sites by Ecoregion

  19. Reference Sites Used to • Score Benthic IBI metrics • Set Good, Fair, Poor condition categories for • Biotic Integrity • Nutrients • Physical Habitat • Predictive (O/E) modeling • Required dropping state augment data

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