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Prioritizing Great Lakes 
      Restoration
          David Allan
     The University of Michigan
                  y         g




                        www.epa.gov/glnpo/image/
                        www.glfc.org/multimedia/photos.php#
Road Map
                  Road Map
• Threats to the Lakes: an overview
  Threats to the Lakes:  an overview

• Assessing the relative magnitude and 
         i    h     l i        i d      d
  spatial distribution of multiple stressors –
  Project GLEAM
  P j GLEAM

• Prioritizing Great Lakes restoration and 
  conservation opportunities
                  pp
Threats to the Lakes: An Overview
 Threats to the Lakes: An Overview
• Diverse
  – Nonpoint runoff, toxics, invasives, development
• Changing in importance over time
  Changing in importance over time
  – May be diminishing, stable, or increasing
• Differ by location
  – E.g., upper vs. lower lakes
• Multiple stressors are at work, and their 
  relative strength varies from place to place
                g               p        p
Environmental Stressors
         Environmental Stressors
• An environmental stressor is a variable which, owing to 
      e    o e a s esso s a a ab e            c ,o g o
  human activity, exceeds its range of normal variation, 
  affecting species, biological communities, or ecosystems
• The source of the stressor is the human activity causing 
  the stress
• Ecological indicators (biodiversity, ecosystem function) 
  help establish a stressor  response relationship
Categories of Stressors
          Categories of Stressors
•   Runoff from the land
    Runoff from the land
•   Toxic chemicals
•   Fishing pressure
     i hi
•   Invasive species
•   Coastal development/Habitat loss
•   Water withdrawal
    Water withdrawal
•   Climate change
Multiple Stressors
             Multiple Stressors
• We’ve just seen seven broad categories of
  We ve just seen seven broad categories of 
  stressors
  – Each includes many specific stressors
    Each includes many specific stressors
  – Some are likely to be more important than others
  – Few (any?) will be equal everywhere
    Few (any?) will be equal everywhere
• How do we assess the cumulative influence 
  of multiple stressors across the Laurentian 
  of multiple stressors across the Laurentian
  Great Lakes?
Project GLEAM:  Mapping 
Individual Stressors Across the 
         Great Lakes 
         Great Lakes
  A AN, J. ., SMITH, S. .P., MCINTYR , P. ., HA P RN,
  ALLAN, J.D., SMITH, S.D.P., MCINTYRE, P.B., HALPERN, 
      B., BOYER, G., BUCHSBAUM, A., BURTON, A., 
    CAMPBELL, L., CHADDERTON, L., CIBOROWSKI, J., 
     DORAN, P., EDER, T., INFANTE, D., JOHNSON, L., 
    LODGE, D., READ, J., RUTHERFORD, E., SOWA, S., 
    LODGE D READ J RUTHERFORD E SOWA S
       STEINMAN, A., JOSEPH, C. And MARINO, A. 
GLEAM Overview
             GLEAM Overview
Great Lakes Environmental Assessment & Mapping 
Great Lakes Environmental Assessment & Mapping
  project
• Map the intensity of multiple stressors across the
  Map the intensity of multiple stressors across the 
  Great Lakes (1‐km2 resolution)
• Develop weightings of relative impact of each 
  stressor by habitat type, based on expert judgment
• Derive a cumulative stress map summing all 
  individual stressors
Choice of Stressors
             Choice of Stressors
Key stressor characteristics:

• Mappable at 1 km2 resolution


• Coverage for all 5 lakes
  Co e age o a 5 a es


• Distinct pathway of impact from other stressors
Stressor Progress
CATEGORY     STRESSOR                                          CATEGORY      STRESSOR
             Hypoxia (low oxygen)
             Hypoxia (low oxygen)                                            Invasive zebra and quagga mussels
                                                                             Invasive zebra and quagga mussels
             Light pollution                                                 Ballast water invasion risk
             Channel dredging                                                Invasive sea lamprey
             Shipping Lanes                                                  Emerging fish diseases (VHS, etc.)
                                                               Invasive and 
   Aquatic 
    q                   p
             Industrial ports and harbors                                                      p       (    g    ,    )
                                                                             Invasive wetland plants (Phragmites, etc.)
                                                                 Nuisance
   Habitat   Tributary dams (altered flow/sediment retention                 Invasive nearshore plants (Eurasian milfoil, etc.)
                                                                  Species
 Alterations Tributary dams (barriers to fish passage)                       Harmful algal blooms (Microcystis, etc.)
             Shoreline hardening                                             Nuisance benthic algal blooms (Cladophora, etc.)
             Shoreline extensions (docks, piers, etc.)                       Invasive plankton (Hemimysis, etc.)
             Submerged cables and pipelines                                  Invasive fish (round goby, etc.)
             Marinas and recreational boating                                Nitrogen loading
             Warming water temperatures                          Nonpoint  Phosphorus loading
   Climate 
             Decreasing ice cover                                 Source     Sediment loading (tributary)
        g
   Change
             Changing water levels
             Ch i          t l l                                 Pollution
                                                                 P ll ti     Combined sewer overflows (CSOs)
                                                                             C bi d                 fl    (CSO )
             Coastal road density                                            Pharmaceutical loading
             Coastal development (residential, commercial)                   Areas of Concern (AOCs)
   Coastal 
             Coastal mining                                                  Toxic metals – biomagnifying (mercury, etc.) 
Development
             Coastal power plants
             Coastal power plants                                  Toxic     Toxic pesticides (Atrazine, etc.)
                                                                             Toxic pesticides (Atrazine etc )
             Coastal recreational use (swimming, etc.)           Chemical  Toxic metals – non‐biomagnifying (copper, etc.)
             Aquaculture                                         Pollution   Toxic organics – biomagnifying (PCBs, etc.)
             Commercial fishing                                              Toxic organics – non‐biomagnifying (PAHs, etc.)
             Recreational fishing (charter)                                  Emerging toxic chemicals (PBDEs, etc.)
  Fisheries 
  Fisheries
             Recreational fishing (non‐charter)                    Water     Water withdrawals  (inland and groundwater)
Management
             Native fish stocking                              Withdrawals Water withdrawals (Great Lakes)
             Non‐native fish stocking                                                                       Not completed/not 
                                                                    Completed            In progress
             Diporeia decline                                                                                    feasible
Survey: Relative impact of stressors
We surveyed experts to weight individual stressors.  
     We want weightings that are:
‐ Stressor specific
   ‐ e.g., mercury is twice as harmful as nitrogen
‐ Habitat specific
   ‐ e.g., mercury in wetlands is twice as harmful as mercury in 
     open water
     open water
‐ Quantitative
   ‐ “Ecosystem impact” is quantified for 5 criteria: temporal 
     frequency, spatial extent, ecological scope, magnitude of 
     change, recovery time
   ‐ Survey uses scenario comparisons to elicit how to combine 
          y                      p
     these criteria for overall impact
                                                                    11
Cumulative Stress
‐ For each stressor, cumulative stress (CS) merges
   ‐ Intensity value for each pixel from stressor map (Si)
   ‐ Relative weight of each stressor from expert survey (Wi)
     Relative weight of each stressor from expert survey

‐ Intensity and weight are normalized to 0‐1 range
‐ Sum across all stressors

  CS = Sum (Si ∙ Wi)
GLRI Priority: 
Working with 
partners on 
outreach




              Prioritizing Restoration and 
              Conservation Opportunities
                   Some closing thoughts
Unique Challenges
            Unique Challenges
• Scale
  – The Great Lakes are large relative to most other 
    restoration targets
    restoration targets


• Complexity
  – The Great Lakes face a wider range of threats 
    relative to most other restoration targets
    relative to most other restoration targets
Image courtesy
Michigan Sea Grant
The Value of Data
            The Value of Data
Of the most important threats:
Of the most important threats:
  – Which are most important? And where?
  – How does the ranking of threats vary from 
                        g               y
    nearshore to offshore, from the upper lakes to the 
    lower lakes?
  – What is the cumulative influence of multiple 
      h      h       l        fl      f    l l
    threats?
• Where are our restoration priorities?
  Where are our restoration priorities?
• Where are our conservation priorities
Guiding Principles
            Guiding Principles
• Clarity of goals
  Clarity of goals
  – What do we want to achieve? What is feasible to 
    achieve?  Who are  we ?
    achieve? Who are “we”?
• Best practices are identified, agreed upon and 
  followed
• Success is evaluated using metrics of 
  ecological condition
      l i l      diti
• The ecosystem is self‐sustaining
A Restoration Strategy
           A Restoration Strategy
• Follow the Precautionary Principle – don’t allow
  Follow the Precautionary Principle  don t allow 
  restoration to become crisis management
• Prioritize risk identify the greatest threats
  Prioritize risk – identify the greatest threats
• Place matters – recognize that the types and level of 
  threat varies with location
   h        i    i hl     i
• Networking is critical – rapid progress depends on 
  sharing of data, methods and ideas 
With the help of many!
• Core Working Group
• Key team members
                b
  – S. Smith, P. McIntyre, C. Joseph, A. Marino, A. Prusevich
  – Students: R. Biel, J. Olson, K. Hanson
    Students: R. Biel, J. Olson, K. Hanson
• Data providers
  – Dozens of staff from GLERL, USGS, Environment Canada, OMNR, 
    USFWS, TNC, GLFC, MDNRE, IFR, GLEI, NFHAP
  – Academic scientists from USA & Canada
              Suggestions or Data to Share?
              Suggestions or Data to Share?
                sdpsmith AT umich.edu
                  dallan AT umich.edu

          http://www.greatlakesmapping.org                         19

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How 2011 abbr_gleam_public_pdf_forslideshare

  • 1. Prioritizing Great Lakes  Restoration David Allan The University of Michigan y g www.epa.gov/glnpo/image/ www.glfc.org/multimedia/photos.php#
  • 2. Road Map Road Map • Threats to the Lakes: an overview Threats to the Lakes:  an overview • Assessing the relative magnitude and  i h l i i d d spatial distribution of multiple stressors – Project GLEAM P j GLEAM • Prioritizing Great Lakes restoration and  conservation opportunities pp
  • 3. Threats to the Lakes: An Overview Threats to the Lakes: An Overview • Diverse – Nonpoint runoff, toxics, invasives, development • Changing in importance over time Changing in importance over time – May be diminishing, stable, or increasing • Differ by location – E.g., upper vs. lower lakes • Multiple stressors are at work, and their  relative strength varies from place to place g p p
  • 4. Environmental Stressors Environmental Stressors • An environmental stressor is a variable which, owing to  e o e a s esso s a a ab e c ,o g o human activity, exceeds its range of normal variation,  affecting species, biological communities, or ecosystems • The source of the stressor is the human activity causing  the stress • Ecological indicators (biodiversity, ecosystem function)  help establish a stressor  response relationship
  • 5. Categories of Stressors Categories of Stressors • Runoff from the land Runoff from the land • Toxic chemicals • Fishing pressure i hi • Invasive species • Coastal development/Habitat loss • Water withdrawal Water withdrawal • Climate change
  • 6. Multiple Stressors Multiple Stressors • We’ve just seen seven broad categories of We ve just seen seven broad categories of  stressors – Each includes many specific stressors Each includes many specific stressors – Some are likely to be more important than others – Few (any?) will be equal everywhere Few (any?) will be equal everywhere • How do we assess the cumulative influence  of multiple stressors across the Laurentian  of multiple stressors across the Laurentian Great Lakes?
  • 7. Project GLEAM:  Mapping  Individual Stressors Across the  Great Lakes  Great Lakes A AN, J. ., SMITH, S. .P., MCINTYR , P. ., HA P RN, ALLAN, J.D., SMITH, S.D.P., MCINTYRE, P.B., HALPERN,  B., BOYER, G., BUCHSBAUM, A., BURTON, A.,  CAMPBELL, L., CHADDERTON, L., CIBOROWSKI, J.,  DORAN, P., EDER, T., INFANTE, D., JOHNSON, L.,  LODGE, D., READ, J., RUTHERFORD, E., SOWA, S.,  LODGE D READ J RUTHERFORD E SOWA S STEINMAN, A., JOSEPH, C. And MARINO, A. 
  • 8. GLEAM Overview GLEAM Overview Great Lakes Environmental Assessment & Mapping  Great Lakes Environmental Assessment & Mapping project • Map the intensity of multiple stressors across the Map the intensity of multiple stressors across the  Great Lakes (1‐km2 resolution) • Develop weightings of relative impact of each  stressor by habitat type, based on expert judgment • Derive a cumulative stress map summing all  individual stressors
  • 9. Choice of Stressors Choice of Stressors Key stressor characteristics: • Mappable at 1 km2 resolution • Coverage for all 5 lakes Co e age o a 5 a es • Distinct pathway of impact from other stressors
  • 10. Stressor Progress CATEGORY STRESSOR CATEGORY STRESSOR Hypoxia (low oxygen) Hypoxia (low oxygen) Invasive zebra and quagga mussels Invasive zebra and quagga mussels Light pollution Ballast water invasion risk Channel dredging Invasive sea lamprey Shipping Lanes Emerging fish diseases (VHS, etc.) Invasive and  Aquatic  q p Industrial ports and harbors p ( g , ) Invasive wetland plants (Phragmites, etc.) Nuisance Habitat  Tributary dams (altered flow/sediment retention Invasive nearshore plants (Eurasian milfoil, etc.) Species Alterations Tributary dams (barriers to fish passage) Harmful algal blooms (Microcystis, etc.) Shoreline hardening Nuisance benthic algal blooms (Cladophora, etc.) Shoreline extensions (docks, piers, etc.) Invasive plankton (Hemimysis, etc.) Submerged cables and pipelines Invasive fish (round goby, etc.) Marinas and recreational boating Nitrogen loading Warming water temperatures Nonpoint  Phosphorus loading Climate  Decreasing ice cover Source Sediment loading (tributary) g Change Changing water levels Ch i t l l Pollution P ll ti Combined sewer overflows (CSOs) C bi d fl (CSO ) Coastal road density Pharmaceutical loading Coastal development (residential, commercial) Areas of Concern (AOCs) Coastal  Coastal mining Toxic metals – biomagnifying (mercury, etc.)  Development Coastal power plants Coastal power plants Toxic Toxic pesticides (Atrazine, etc.) Toxic pesticides (Atrazine etc ) Coastal recreational use (swimming, etc.) Chemical  Toxic metals – non‐biomagnifying (copper, etc.) Aquaculture Pollution Toxic organics – biomagnifying (PCBs, etc.) Commercial fishing Toxic organics – non‐biomagnifying (PAHs, etc.) Recreational fishing (charter) Emerging toxic chemicals (PBDEs, etc.) Fisheries  Fisheries Recreational fishing (non‐charter) Water  Water withdrawals  (inland and groundwater) Management Native fish stocking Withdrawals Water withdrawals (Great Lakes) Non‐native fish stocking Not completed/not  Completed In progress Diporeia decline feasible
  • 11. Survey: Relative impact of stressors We surveyed experts to weight individual stressors.   We want weightings that are: ‐ Stressor specific ‐ e.g., mercury is twice as harmful as nitrogen ‐ Habitat specific ‐ e.g., mercury in wetlands is twice as harmful as mercury in  open water open water ‐ Quantitative ‐ “Ecosystem impact” is quantified for 5 criteria: temporal  frequency, spatial extent, ecological scope, magnitude of  change, recovery time ‐ Survey uses scenario comparisons to elicit how to combine  y p these criteria for overall impact 11
  • 12. Cumulative Stress ‐ For each stressor, cumulative stress (CS) merges ‐ Intensity value for each pixel from stressor map (Si) ‐ Relative weight of each stressor from expert survey (Wi) Relative weight of each stressor from expert survey ‐ Intensity and weight are normalized to 0‐1 range ‐ Sum across all stressors CS = Sum (Si ∙ Wi)
  • 13. GLRI Priority:  Working with  partners on  outreach Prioritizing Restoration and  Conservation Opportunities Some closing thoughts
  • 14. Unique Challenges Unique Challenges • Scale – The Great Lakes are large relative to most other  restoration targets restoration targets • Complexity – The Great Lakes face a wider range of threats  relative to most other restoration targets relative to most other restoration targets
  • 16. The Value of Data The Value of Data Of the most important threats: Of the most important threats: – Which are most important? And where? – How does the ranking of threats vary from  g y nearshore to offshore, from the upper lakes to the  lower lakes? – What is the cumulative influence of multiple  h h l fl f l l threats? • Where are our restoration priorities? Where are our restoration priorities? • Where are our conservation priorities
  • 17. Guiding Principles Guiding Principles • Clarity of goals Clarity of goals – What do we want to achieve? What is feasible to  achieve?  Who are  we ? achieve? Who are “we”? • Best practices are identified, agreed upon and  followed • Success is evaluated using metrics of  ecological condition l i l diti • The ecosystem is self‐sustaining
  • 18. A Restoration Strategy A Restoration Strategy • Follow the Precautionary Principle – don’t allow Follow the Precautionary Principle  don t allow  restoration to become crisis management • Prioritize risk identify the greatest threats Prioritize risk – identify the greatest threats • Place matters – recognize that the types and level of  threat varies with location h i i hl i • Networking is critical – rapid progress depends on  sharing of data, methods and ideas 
  • 19. With the help of many! • Core Working Group • Key team members b – S. Smith, P. McIntyre, C. Joseph, A. Marino, A. Prusevich – Students: R. Biel, J. Olson, K. Hanson Students: R. Biel, J. Olson, K. Hanson • Data providers – Dozens of staff from GLERL, USGS, Environment Canada, OMNR,  USFWS, TNC, GLFC, MDNRE, IFR, GLEI, NFHAP – Academic scientists from USA & Canada Suggestions or Data to Share? Suggestions or Data to Share? sdpsmith AT umich.edu dallan AT umich.edu http://www.greatlakesmapping.org 19