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Gulf of Mexico Hypoxia Assessment Plan Committee on Environment and Natural Resources Hypoxia Work G

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Title: Gulf of Mexico Hypoxia Assessment Plan Committee on Environment and Natural Resources Hypoxia Work G


1
Gulf of Mexico Hypoxia Assessment PlanCommittee
on Environment and Natural ResourcesHypoxia Work
Group
  • Topic 4 Effects of Nutrient Load Reductions
  • David W. Dilks (Presenter)
  • Patrick L. Brezonik (Watershed P. I.)
  • Victor J. Bierman, Jr. (Gulf of Mexico P. I.)

2
Objectives
  • Evaluate the effect of nutrient-source reductions
    that may be implemented in the Mississippi River
    Basin on
  • Water quality in the drainage basin itself
  • Water quality in the nearshore Gulf waters

3
Study Questions
  • What are the effects of reducing MRB nutrient
    loads on
  • Nutrient concentration in the flowing waters of
    the basin?
  • Water quality and ecological condition in the
    flowing waters of the basin?
  • Dissolved oxygen and chlorophyll on the LIS?
  • What magnitude of reductions in nutrient loadings
    might be necessary to improve present water
    quality conditions, especially seasonal hypoxia?

4
Watershed Approach
  • Consider both nitrogen and phosphorus
  • Case study on Minnesota River examining
    effectiveness of improved management practices
  • Examine nutrient retention in the flowing waters
    of the Mississippi River Basin
  • Examine benefit of lower nutrient concentrations
    on ecosystem and water quality

5
Gulf of Mexico Approach
  • Develop deterministic water quality model of the
    Louisiana Inner Shelf portion of the Gulf of
    Mexico
  • WASP model
  • Relatively simple kinetic complexity
  • Externally specified hydrodynamics
  • Apply model to investigate relationship between
    nutrient load reductions and dissolved oxygen/
    chlorophyll a concentrations on the LIS

6
Sediment Flux
Boundary Conditions
Advection and Dispersion
External Source Loads
Light
Temperature
Water Column
Denitrification
Organic C
NO2 NO3
NH3
SRP
Reaeration
Denitrification
Settling
Organic P
OrganicN
Nitrification
Oxidation
Settling
Settling
Photosynthesis
Phyto- plankton
Zoo- plankton
Dissolved Oxygen
Grazing
Respiration
Respiration / Decay
Settling
SOD
Sediment
7
Watershed Findings
  • Nutrient loss processes from agricultural lands
    differ between N and P
  • N Subsurface drainage
  • P Erosion
  • Water quality standards violations are rare, but
    proposed nutrient criteria routinely exceeded
  • River productivity correlated to phosphorus

8
Gulf Findings
  • Dissolved oxygen and chlorophyll a on the LIS
    appear to be sensitive to changes in nutrient
    loads
  • Nitrogen more important than phosphorus
  • A 20-30 reduction in TN loads could increase
    bottom water dissolved oxygen by 15 to 50
  • Sensitivity analyses conducted to determine
    primary sources of uncertainty
  • seaward boundary conditions underwater light
    attenuation sediment oxygen demand variability
    in hydrometeorology

9
(No Transcript)
10
Average Dissolved Oxygen Responses1985 - N
Reductions
11
Average Dissolved Oxygen ResponsesN Reductions -
All Boundaries Reduced
12
Dissolved Oxygen Sensitivity Analyses1990
Conditions
450
30
400
-30
350
300
250
200
150
Percent of Baseline
100
50
0
-50
-100
Extinction
Saturation
Carbon
Water
Sediment
Extinction
Saturation
Carbon
Water
Sediment
Coefficient
Light
Chlorophyll
Column
Oxygen
Coefficient
Light
Chlorophyll
Column
Oxygen
Intensity
Ratio
Oxygen
Demand
Intensity
Ratio
Oxygen
Demand
Demand
Demand
13
Basin Monitoring Recommendations
  • Routine monitoring programs by local, state and
    federal agencies are essential should be
    continued
  • Additional monitoring sites are needed in the
    Upper Mississippi main channel to evaluate
    nutrient retention/loss in the lock and dam
    system.
  • Monitoring needs to be expanded in the Lower
    Mississippi to clarify the extent of nutrient
    retention.

14
Basin Monitoring Recommendations
  • Better monitoring is needed at fine spatial
    scales to establish effects of changes in land
    management on nutrient loads
  • Long-term, intensive monitoring/research sites
    should be established at the field/minor
    watershed scale
  • Monitoring fertilizer use patterns is critical
    for targeting improvements in management
    practices within identified problem areas

15
Basin Research Recommendations
  • Studies on improved management practices to
    minimize off-site impacts of agricultural
    production
  • Research on impacts of large confined-animal-feedi
    ng-operations (CAFOs) and ways to minimize
  • Better information on rates of nitrification and
    denitrification and factors affecting these
    processes
  • Information on mechanisms of P retention and
    factors affecting these processes

16
Basin Research Recommendations
  • Assess whether the mechanism(s) causing shifts
    towards dominance of plankton by blue-green algae
    in eutrophic rivers are the same as or different
    from those causing blue-green blooms in lakes
  • N- vs. P-limitation should be assessed by
    bioassays and algal tissue analysis
  • Importance of light vs. nutrient limitation of
    algal growth in rivers needs to be assessed
  • Critical nutrient concentrations and loading
    rates need to be developed for flowing waters

17
Basin Modeling Recommendations
  • Further development and field testing of the
    SWAT-based, national- scale model for nutrient
    export and transport should be pursued
  • Further development of regression-based models
    relating nutrient-related variables to stream
    trophic state and nutrient loading from the
    watershed
  • Further modeling efforts are needed in extending
    the chemical reactor modeling approach of
    Vollenweider to rivers, for both N and P
  • The N/P ratio hypothesis needs further
    clarification

18
Basin Modeling Recommendations
  • Models for algal growth in rivers should focus on
    peak biomass, not only on mean annual biomass
  • Models should be developed at different levels of
    complexityfrom spreadsheet to complex simulation
    modelsto relate watershed export and stream
    nutrient concentrations and transport in the MRB
  • Models to predict effects of changes in river
    nutrient levels on fish yield or fish species
    composition are lacking, and should be developed

19
Gulf Monitoring Recommendations
  • Future monitoring design should be driven by
    management questions, and should be based on a
    quantitative ecosystem model
  • Monitoring should be conducted on a hierarchy of
    spatial scales, temporal scales and parameters
  • There is a basic need for physical oceanographic
    data on water movements

20
Gulf Monitoring Recommendations
  • Data needed on light attenuation and other
    correlated parameters
  • In-situ measures of primary productivity
  • Comprehensive data specifying external model
    forcing functions

21
Gulf Research Recommendations
  • Emphasis should be placed on better defining
    physical, chemical and biological processes
  • Primary productivity
  • Indigenous species, light dependency
  • Factors controlling underwater light attenuation
  • Fate pathways for organic carbon
  • Cycling and transformation of nutrients, carbon
    and oxygen
  • Sediment processes and sediment-water
    interactions
  • Shifts in phytoplankton species abundance

22
Gulf Modeling Recommendations
  • The water quality model should be directly
    coupled with a hydrodynamic model
  • The temporal domain should be extended to include
    continuous representation of water quality
    conditions
  • The spatial domain should be extended to include
    entire Gulf of Mexico

23
Gulf Modeling Recommendations
  • The horizontal and vertical spatial resolution
    should be refined
  • A sediment diagenesis submodel is needed
  • The model should be expanded to include multiple
    phytoplankton groups and silicon
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