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Looking Inland: Ohio Reservoir Water
Quality




                                      Joe Conroy
                               Fisheries Biologist
                   Inland Fisheries Research Unit
Variable sportfish recruitment & survival
           Variable sportfish recruitment
              & survival environment


Land use   +   Shape   +   Productivity   +   Zooplankton   +   Forage fish

                                                  +
 Understand sportfish variability by
 understanding system variability?
Understanding productivity variation
   Known governing factors
    » Land cover/use
       – External effects

    » Reservoir type

       – Internal effects

   Seek state-wide baseline
    »   Ongoing perturbations
        – Reservoir aging

        – Watershed modification



Goal: Assess productivity trends among
reservoirs
Roadmap

   Conceptualizing sportfish variability

   Compiling productivity data

   Comparing reservoir productivity
Roadmap

   Conceptualizing sportfish variability

   Compiling productivity data: 212 “snapshots”

   Comparing reservoir productivity
Ohio Reservoir Productivity Database
   ORPAD built in 2006
    » Manage project-specific data
    » Archive all inland data



   Stores:
    » 2,151 trips (1993–2011)
    » 153 reservoirs

    » 3,606 samples (1,416 “complete”)

       – SD, TSS, TN, TP, Chl
Assessing state-wide trends
   Extensive reservoir set
    »   n = 134
   Summer sampling
    » July and/or August
    » 2006 and/or 2007

       – n = 90 res in 2006

       – n = 80 res in 2007

    » n = 212 res-yrs




        Compare reservoir productivity
        statewide
Assessing trends: Productivity metrics
   Synthetic examination
    » Secchi transparency; SD
    » [Total suspended sediment]; TSS

    » [Non-volatile suspended sediment]; NVSS

    » [Total phosphorus]; TP

    » [Total nitrogen]; TN

    » [Chlorophyll a]; Chl
Assessing trends: Detecting a signal
   Decrease data dimension (6D  1D), examine pattern

   Predictors: Ensure multivariate normality; ordinate
    » Variables summarized by reservoir; log-transformed
    » NVSS not retained; non-normal data

    » Principal components analysis conducted




   Results: Examine ordination
    »   Generate composite productivity variable
Roadmap

   Conceptualizing sportfish variability

   Compiling productivity data

   Comparing reservoir productivity
Roadmap

   Conceptualizing sportfish variability

   Compiling productivity data

   Comparing reservoir productivity: One axis
One composite productivity variable
   Principal components analysis
    »   1D solution (λ = 3.81, R2 = 76.2%)
          23650      0.380.9   1306139 11.3715.3 3.4351.9




    » PC score re-centered and relativized: 01 scale
    » Ranked reservoirs (1134, hypereutrophicoligotrophic)
Statewide comparison
   Secchi transparency (cm)
Statewide comparison
 Secchi transparency (cm)
 Total P (mg/m3)
Statewide comparison
 Secchi transparency (cm)
 Total P (mg/m3)

 Chlorophyll a (mg/m3)
Statewide comparison
 Secchi transparency (cm)
 Total P (mg/m3)

 Chlorophyll a (mg/m3)

 Rank
Leveraging reservoir productivity data
   Assessing change                1992
    » Land use/cover change
       –  Urban,  Row crops

    » Reservoir aging

       –  Volume,  Productivity

        Modify fish habitat &
        ecosystem function                 2006




>5
yd3/ac/y               < 0.1
                       yd3/ac/y
Limno/Lower Trophic Team
   Marty Lundquist
   Joel Plott
   Matt Wolfe
   Don Swatzel
   Glenn Trueb

Research Partners
Miami University
 Mike Vanni

 Maria González

The Ohio State University
 Dave Culver

 Stu Ludsin

 Ruth Briland, Sarah Wallace,
  Cathy Doyle, Mike Kulasa

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Looking Inland: Ohio Reservoir Water Quality

  • 1. Looking Inland: Ohio Reservoir Water Quality Joe Conroy Fisheries Biologist Inland Fisheries Research Unit
  • 2. Variable sportfish recruitment & survival Variable sportfish recruitment & survival environment Land use + Shape + Productivity + Zooplankton + Forage fish + Understand sportfish variability by understanding system variability?
  • 3. Understanding productivity variation  Known governing factors » Land cover/use – External effects » Reservoir type – Internal effects  Seek state-wide baseline » Ongoing perturbations – Reservoir aging – Watershed modification Goal: Assess productivity trends among reservoirs
  • 4. Roadmap  Conceptualizing sportfish variability  Compiling productivity data  Comparing reservoir productivity
  • 5. Roadmap  Conceptualizing sportfish variability  Compiling productivity data: 212 “snapshots”  Comparing reservoir productivity
  • 6. Ohio Reservoir Productivity Database  ORPAD built in 2006 » Manage project-specific data » Archive all inland data  Stores: » 2,151 trips (1993–2011) » 153 reservoirs » 3,606 samples (1,416 “complete”) – SD, TSS, TN, TP, Chl
  • 7. Assessing state-wide trends  Extensive reservoir set » n = 134  Summer sampling » July and/or August » 2006 and/or 2007 – n = 90 res in 2006 – n = 80 res in 2007 » n = 212 res-yrs Compare reservoir productivity statewide
  • 8. Assessing trends: Productivity metrics  Synthetic examination » Secchi transparency; SD » [Total suspended sediment]; TSS » [Non-volatile suspended sediment]; NVSS » [Total phosphorus]; TP » [Total nitrogen]; TN » [Chlorophyll a]; Chl
  • 9. Assessing trends: Detecting a signal  Decrease data dimension (6D  1D), examine pattern  Predictors: Ensure multivariate normality; ordinate » Variables summarized by reservoir; log-transformed » NVSS not retained; non-normal data » Principal components analysis conducted  Results: Examine ordination » Generate composite productivity variable
  • 10. Roadmap  Conceptualizing sportfish variability  Compiling productivity data  Comparing reservoir productivity
  • 11. Roadmap  Conceptualizing sportfish variability  Compiling productivity data  Comparing reservoir productivity: One axis
  • 12. One composite productivity variable  Principal components analysis » 1D solution (λ = 3.81, R2 = 76.2%) 23650 0.380.9 1306139 11.3715.3 3.4351.9 » PC score re-centered and relativized: 01 scale » Ranked reservoirs (1134, hypereutrophicoligotrophic)
  • 13. Statewide comparison  Secchi transparency (cm)
  • 14. Statewide comparison  Secchi transparency (cm)  Total P (mg/m3)
  • 15. Statewide comparison  Secchi transparency (cm)  Total P (mg/m3)  Chlorophyll a (mg/m3)
  • 16. Statewide comparison  Secchi transparency (cm)  Total P (mg/m3)  Chlorophyll a (mg/m3)  Rank
  • 17. Leveraging reservoir productivity data  Assessing change 1992 » Land use/cover change –  Urban,  Row crops » Reservoir aging –  Volume,  Productivity Modify fish habitat & ecosystem function 2006 >5 yd3/ac/y < 0.1 yd3/ac/y
  • 18. Limno/Lower Trophic Team  Marty Lundquist  Joel Plott  Matt Wolfe  Don Swatzel  Glenn Trueb Research Partners Miami University  Mike Vanni  Maria González The Ohio State University  Dave Culver  Stu Ludsin  Ruth Briland, Sarah Wallace, Cathy Doyle, Mike Kulasa

Notas del editor

  1. Contains ~ 18,400 depth-specific measurements, 1,821 Secchi transparency measurements, 2,270 TSS measurements, 2,745 TP measurements, and 2,014 Chla measurements.Of the 3,262 samples, 1,479 are “complete” (SD, TSS, TP, Chl &gt; 0) with 1,033 are from non-Inflow sites (Outflow + Mid-lake), and 796 are from 2006-present (= Program).Of the 3,262 samples, 1,061 are from Intensive reservoirs with 663 from non-Inflow sites (Outflow + Mid-lake), and 435 were collected from 2006-present.
  2. Intensive reservoir characteristics:SA: 256-1328 ha (632-3280 acres); zmax = 4.8-20.9 m; WA:SA: 21-293