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Sampling issues in river health
assessment
Dr Chris Gippel, Australia

Workshop on China’s national river health assessment program

Ministry of Water Resources
2012 February 22
Low                             Sensitivity to change                 High

                                          Scale
100 – 1,000,000 km2 10 – 1000 km2      100 – 10,000 m       1 – 100 m   0.1 – 1.0 m




   Basin and      Functional process       Reach              Site       Microhabitat
   catchment             zone

       Report aggregated                    Report individual
          site scores                         site scores
Border Rivers




Fish              Macroinvertebrates
How many sites?
•   Murray-Darling Basin
     – 1,061,469 km2
     – 506 fish sites; 773 invertebrate sites
         • 1 site per 2,100 km2 for fish
         • 1 site per 1,370 km2 for macroinvertebrates
•   Victoria
     – 227,416 km2
     – 1,040 reaches/sites
         • 1 site per 219 km2
•   SE Queensland
     – 22,420 km2
     – 135 sites
         • 1 site per 166 km2
How many sites?
•   Budget
•   Objective
    – Confirm known issues (e.g. sewerage pollution)
        • Wherever the issues are located
    – Monitor catchment health change over time
        • Sufficient statistical power to detect change
Variation in space   Variation in time

                               low                     low
           few




                               low                     high

    Number of
  sites required
to detect change
                                high                  low




                               high                    high
        many
How often to sample?
•   Budget
•   Objective
    – Seasonal variation important (depends on system)
        – 2 times per year
    – Fit in with annual reporting schedules
        – 1 or 2 times per year
    – Long term change is main priority
        – Every 2 – 5 years
    – Slowly changing parameters (e.g. vegetation, physical form)
        – Every 2 – 5 years
Where to locate the sites?
•   Budget
•   Objective

•   Random
     – Most expensive
     – Most statistically sound
     – Mix of fixed and non-fixed sites
•   Stratified
     – Freedom to chose exact site within a specified zone
•   Non-random
     –   “Data hunting” – looking for evidence of known issues
     –   Avoiding sites with poor health
     –   Selecting only large rivers, or high profile sites
     –   Risk of systematic bias (e.g. all sites near roads or bridges)
Sampling at the chosen site
•   If chosen because of easy access, avoid unusual activity:
     –   vehicles crossing the stream;
     –   waste disposal;
     –   recreational angling;
     –   sand and gravel extraction;
     –   timber collection;
     –   washing clothing and vegetables
•   Follow standard protocols
Summary
•   Sampling strategy depends on:
     –   Budget
     –   Objectives
     –   Expected variability of the data
     –   Reporting scale

     Need to establish these things before setting the sampling sites

•   Program sampling strategy should be designed by a statistician
     – As a minimum, report the sampling strategy


•   Follow standard protocols at the site

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5.1 sampling issues in river health assessment en

  • 1. Sampling issues in river health assessment Dr Chris Gippel, Australia Workshop on China’s national river health assessment program Ministry of Water Resources 2012 February 22
  • 2. Low Sensitivity to change High Scale 100 – 1,000,000 km2 10 – 1000 km2 100 – 10,000 m 1 – 100 m 0.1 – 1.0 m Basin and Functional process Reach Site Microhabitat catchment zone Report aggregated Report individual site scores site scores
  • 3. Border Rivers Fish Macroinvertebrates
  • 4.
  • 5.
  • 6. How many sites? • Murray-Darling Basin – 1,061,469 km2 – 506 fish sites; 773 invertebrate sites • 1 site per 2,100 km2 for fish • 1 site per 1,370 km2 for macroinvertebrates • Victoria – 227,416 km2 – 1,040 reaches/sites • 1 site per 219 km2 • SE Queensland – 22,420 km2 – 135 sites • 1 site per 166 km2
  • 7. How many sites? • Budget • Objective – Confirm known issues (e.g. sewerage pollution) • Wherever the issues are located – Monitor catchment health change over time • Sufficient statistical power to detect change
  • 8. Variation in space Variation in time low low few low high Number of sites required to detect change high low high high many
  • 9. How often to sample? • Budget • Objective – Seasonal variation important (depends on system) – 2 times per year – Fit in with annual reporting schedules – 1 or 2 times per year – Long term change is main priority – Every 2 – 5 years – Slowly changing parameters (e.g. vegetation, physical form) – Every 2 – 5 years
  • 10. Where to locate the sites? • Budget • Objective • Random – Most expensive – Most statistically sound – Mix of fixed and non-fixed sites • Stratified – Freedom to chose exact site within a specified zone • Non-random – “Data hunting” – looking for evidence of known issues – Avoiding sites with poor health – Selecting only large rivers, or high profile sites – Risk of systematic bias (e.g. all sites near roads or bridges)
  • 11. Sampling at the chosen site • If chosen because of easy access, avoid unusual activity: – vehicles crossing the stream; – waste disposal; – recreational angling; – sand and gravel extraction; – timber collection; – washing clothing and vegetables • Follow standard protocols
  • 12.
  • 13.
  • 14. Summary • Sampling strategy depends on: – Budget – Objectives – Expected variability of the data – Reporting scale Need to establish these things before setting the sampling sites • Program sampling strategy should be designed by a statistician – As a minimum, report the sampling strategy • Follow standard protocols at the site