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Some technical and background
information to support
development of river health
assessment programs
Macroinvertebrates as ecological indcators
• Macroinvertebrates most widely used biological
  indicator of stream health
   – Good performance in evaluating WQ, especially heavy
     metals, organic pollution
   – Efficient to sample
   – “Cosmopolitan” – similar groups in different parts of the world

• However:
   – Less sensitive to changes in hydrology and physical form
     (geomorphology)
   – Do not quantify environmental “goods and services” such as
     fisheries production
Two broad approaches
• Multi-variate approaches
  – RIVPACS, AUSRIVAS



• Multi-metric approaches
  – IBI, SIGNAL
Multi-metric indicators (e.g. IBI, SIGNAL)
  1. Combine a number of metrics describing the
     composition and tolerance of the invertebrate
     assemblages at a site.
  2. Individual or combined metric scores compared
     against values derived from geographically similar
     reference sites


  – Multi-metric approach depends on fairly predictable
    patterns of tolerance of different invertebrate taxa
    (often Order/Family) to disturbance gradients
Multivariate indicators (e.g.
RIVPACS, AUSRIVAS)
  1. Use statistical models based on reference sites to
     „predict‟ biota occurring at assessment sites.
  2. Difference between observed (O) and expected (E)
     – (O/E) is used as „indicator.

  – Predictive models replace the use of regionalisation
    in deriving reference values
  – Initial development requires large datasets to build
    and validate statistical models
  – Less transferable than multi-metric methods
AUSRIVAS (Australian River Assessment
System)
• Developed as “Australia-wide” river health
  assessment program
  –   Macroinvertebrates as indicator
  –   Many years of development
  –   Au$Millions
  –   Still being refined

  – Not used in every state.
  – Not the only program of assessment.
Statistical models


Speces occurrence ~ env. Predictor 1 + env. Predictor 2…
Measuring impairment
• OE metric considers taxa predicted to occur
  with a >50% probability based on site
  characteristics
• OE ratio of these taxa used to assess
  impairment of site
Multi-metric (IBI type approaches)
• SIGNAL: Stream
  Invertebrate Grade
  number – Average Level

• Each taxon is given a
  „sensitivity‟ score (0-10)
   – Reported as average score
     of all taxa recorded from a
     site
Information to calculate SIGNAL score
Method includes sampling
recommendations
Manuals provide detailed steps
Detailed data sheets provided for all field
assessments
Technical details vs implementation
• Both „multivariate‟ (e.g. AUSRIVAS) and „multi-
  metric‟ scoring systems (e.g. SIGNAL, B-IBI)
  used in Australia
  – Both approaches shown to be effective at identifying
    polluted sites.
  – Approaches still being refined, especially for desert
    bio-regions

     Technical details of each method are
   important, but both approaches effective if
                properly applied
Chessman (2003) NSW Dept infrastructure
    planning and Natural resources




“We suggest that Australia relies too heavily on bioassessment concepts developed
to assess water pollution in well-watered regions of the Northern Hemisphere.
Effective assessment of human impacts on macroinvertebrates in the rivers of inland
Australia requires a better understanding of the roles of flow regimes, including flood
and drought se- quences, and of microhabitat structure and invasive alien species.”
Reducing variance (s) in the results


  –   Training programs
  –   Accreditation of staff
  –   Web-training, data reporting etc.
  –   QA/QC at every stage of assessment
QA/QC – staff training

• Appropriate training and testing of
  staff involved in field and
  laboratory work
• EPA (Australia) ID 20% of
  invertebrate samples twice for
  consistency.
• Development of standard
  operating procedures
• May involve collaboration between
  organisations -
  universities, research
  groups, central & provincial govt.
AUSRIVAS: online training and accreditation
Summarising experiences from Australia
• River health monitoring and environmental flows
  assessment strategies take considerable time to
  develop, and evolve over time
• 15+ years in Australia (>20 years in USA)
   – Changes in indicators
   – Refinement of targets and scoring systems
• Technical details matter
• Training and QA/QC equally as important to
  success of programs.

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4.1 macro invertebrates as ecological indicators-en

  • 1. Some technical and background information to support development of river health assessment programs
  • 2. Macroinvertebrates as ecological indcators • Macroinvertebrates most widely used biological indicator of stream health – Good performance in evaluating WQ, especially heavy metals, organic pollution – Efficient to sample – “Cosmopolitan” – similar groups in different parts of the world • However: – Less sensitive to changes in hydrology and physical form (geomorphology) – Do not quantify environmental “goods and services” such as fisheries production
  • 3. Two broad approaches • Multi-variate approaches – RIVPACS, AUSRIVAS • Multi-metric approaches – IBI, SIGNAL
  • 4. Multi-metric indicators (e.g. IBI, SIGNAL) 1. Combine a number of metrics describing the composition and tolerance of the invertebrate assemblages at a site. 2. Individual or combined metric scores compared against values derived from geographically similar reference sites – Multi-metric approach depends on fairly predictable patterns of tolerance of different invertebrate taxa (often Order/Family) to disturbance gradients
  • 5. Multivariate indicators (e.g. RIVPACS, AUSRIVAS) 1. Use statistical models based on reference sites to „predict‟ biota occurring at assessment sites. 2. Difference between observed (O) and expected (E) – (O/E) is used as „indicator. – Predictive models replace the use of regionalisation in deriving reference values – Initial development requires large datasets to build and validate statistical models – Less transferable than multi-metric methods
  • 6. AUSRIVAS (Australian River Assessment System) • Developed as “Australia-wide” river health assessment program – Macroinvertebrates as indicator – Many years of development – Au$Millions – Still being refined – Not used in every state. – Not the only program of assessment.
  • 7. Statistical models Speces occurrence ~ env. Predictor 1 + env. Predictor 2…
  • 8. Measuring impairment • OE metric considers taxa predicted to occur with a >50% probability based on site characteristics • OE ratio of these taxa used to assess impairment of site
  • 9. Multi-metric (IBI type approaches) • SIGNAL: Stream Invertebrate Grade number – Average Level • Each taxon is given a „sensitivity‟ score (0-10) – Reported as average score of all taxa recorded from a site
  • 10. Information to calculate SIGNAL score
  • 13. Detailed data sheets provided for all field assessments
  • 14. Technical details vs implementation • Both „multivariate‟ (e.g. AUSRIVAS) and „multi- metric‟ scoring systems (e.g. SIGNAL, B-IBI) used in Australia – Both approaches shown to be effective at identifying polluted sites. – Approaches still being refined, especially for desert bio-regions Technical details of each method are important, but both approaches effective if properly applied
  • 15. Chessman (2003) NSW Dept infrastructure planning and Natural resources “We suggest that Australia relies too heavily on bioassessment concepts developed to assess water pollution in well-watered regions of the Northern Hemisphere. Effective assessment of human impacts on macroinvertebrates in the rivers of inland Australia requires a better understanding of the roles of flow regimes, including flood and drought se- quences, and of microhabitat structure and invasive alien species.”
  • 16. Reducing variance (s) in the results – Training programs – Accreditation of staff – Web-training, data reporting etc. – QA/QC at every stage of assessment
  • 17. QA/QC – staff training • Appropriate training and testing of staff involved in field and laboratory work • EPA (Australia) ID 20% of invertebrate samples twice for consistency. • Development of standard operating procedures • May involve collaboration between organisations - universities, research groups, central & provincial govt.
  • 18. AUSRIVAS: online training and accreditation
  • 19. Summarising experiences from Australia • River health monitoring and environmental flows assessment strategies take considerable time to develop, and evolve over time • 15+ years in Australia (>20 years in USA) – Changes in indicators – Refinement of targets and scoring systems • Technical details matter • Training and QA/QC equally as important to success of programs.