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Office of Research and DevelopmentNational Health and Environmental Effects
Research Laboratory
Office of Research and DevelopmentNational Health and Environmental Effects
Research LaboratoryGulf of Mexico Hypoxia Monitoring &
ModelingGulf of Mexico Hypoxia Monitoring &
Modeling
Water Quality Issues in the Gulf of Mexico
Reduce coastal nutrient loads Reduce hypoxia in northern
Gulf Improve water quality Restore wetlands Preserve habitats
Sources: Gulf Alliance, draft reportNCCR2, 2005Hypoxia Action Plan, 2001
Office of Wetlands, Oceans& WatershedsMS River/Gulf of MexicoWatershed Nutrient Task Force
Office of Science & TechnologyNational Nutrient Criteria
2001 Hypoxia Action called for reassessment in 5 years – assess progress towards goals and revise if needed
SAB will conduct assessment of Gulf hypoxia science (beginning in 2006) - SAB will require information update (GED lead for Hypoxia Science Symposium)
MS River Basin and Gulf receiving water focus for EcoProtection MYP revision
Nutrient criteria recommendations for freshwater systems by ecoregion released in 2001 - States are working to revise FW criteria
OST required to release estuarine nutrient criteria recommendations by 2007
OST required to release nutrient criteria recommendations for wetlands and coastal marine waters by ???
Office of Water Needs
Gulf Hypoxia Monitoring and Modeling
MED Field StationGrosse Ile, MichiganRussell G. Kreis Jr.
Gulf Ecology DivisionGulf Breeze, FloridaRichard M. Greene
Gulf of Mexico Program OfficeStennis, Mississippi
Western Ecology DivisionNewport, OregonPeter M. Eldridge
Office of WaterWashington DC
Gulf Hypoxia Monitoring and ModelingGulf Hypoxia Monitoring and ModelingGoal:Develop consensus modeling framework targeting Gulf hypoxia
o to reduce uncertainty and enhance credibility of model estimates of nutrient load reductions required to meet Action Plan goals
o provide defensible options to guide restoration and decision-making
Goal:Develop consensus modeling framework targeting Gulf hypoxia
o to reduce uncertainty and enhance credibility of model estimates of nutrient load reductions required to meet Action Plan goals
o provide defensible options to guide restoration and decision-making
CENR National HypoxiaAssessment Report (1999)
CENR National HypoxiaAssessment Report (1999)
o Primary obstacle to reducing model uncertainties … is lack of a sufficiently comprehensive database
o Existing database not designed to quantify load-response relationships – new monitoring approaches needed
o Comprehensive monitoring programs alone will not be sufficient for developing, calibrating and validating quantitative WQ models – relevant and targeted research needed
o Future modeling should include linkages of WQ/Eutro and hydrodynamics, expansion of spatial domain, and refinement of temporal and spatial resolution – new integrated, multimedia modeling constructs needed
ORD ObjectivesORD Objectives
• Establish an integrated multimedia, mathematical modeling framework that incorporates monitoring, condition assessment, diagnosis, and research
• Support the framework with a statistically-based, seasonal field monitoring design and targeted research
• Integrate physical, chemical, biological components with external and internal nutrient loads
• Establish stressor-response relationships for nutrient loads & concentrations, Chl a, and DO
• Develop predictive capability to forecast the benefits of risk reduction options and the time to realize the benefits
• Examine stressor-response relationships using forecasting to provide bases for biologically-based, nutrient criteria for ambient nutrients, Chl a, and DO
• Provide managers with defensible methods, tools, and options to aid and guide the environmental decision-making process
ORD Gulf Hypoxia Modeling Framework
SurfaceWaveModel
HydrodynamicModel
AtmosphericTransport
Model
ComputationalTransport
SedimentTransport &
Diagenesis Model
WaterQualityModel
EutrophicationModel
MassBalance
Wave direction,height, period
DepositionFluxes
Advective/DispersiveTransport
DissolvedOxygen Model
(water/sediment)
Meteorological data
ConstituentMass
loadings
Framework ModelsFramework Models
Atmospheric
Hydrodynamic/Meteorological
Sediment transport, fate, and diagenesis
Water Quality/Eutrophication/Dissolved Oxygen
Model Components
ORD/NERL
USN, NRL
ORD/NHEERL
ORD/NHEERL
CMAQ, CTM, MM5
IAS NCOM
IPX-MT andCE-QUAL-ICM hybrid
WASP andCE-QUAL-ICM hybrid
Partners
U.S. EPA-ORD/NERL
Conceptual Relationship Between Maximum Hypoxic Zone Size and
Load Reduction
Establish a defensible nutrient loading target necessary to reduce the areal extent of hypoxic bottom waters in the Gulf
Develop eco-forecasting capabilities to evaluate nutrient management strategies and timelines to achieve results
2000 2005 2010 2015
Hyp
oxi
c A
rea
(10
3 k
m2)
0
10
20
30No Change-20% by 2015 -50% by 2015
Hypoxia Recovery Scenarios Under Gradual Nutrient Reductions and
Hydrologic Variability
Gulf Hypoxia Monitoring SurveysGulf Hypoxia Monitoring SurveysCharacterize the spatial and temporal variability in oceanographic state and process variables, including resolution of the seaward and down-plume boundary conditions of the model domain
Quantify key processes influencing hypoxia to improve predictive models
Develop geo-referenced database to support model development
Gulf Hypoxia Monitoring SurveysGulf Hypoxia Monitoring SurveysSurveys Completed
Dec 2–15 2002March 17–31 2003June 9–23 2003Nov 5–19 2003April 2–7 2004March 21-31 2005Sept 26 – Oct 9, 2005
Station Sampling SummaryCTD CTD+Water Benthic17 19 029 36 626 25 728 42 9 0 22 424 42 10
-94.5 -94 -93.5 -93 -92.5 -92 -91.5 -91 -90.5 -90 -89.5 -89 -88.527.5
28
28.5
29
29.5
30
30.5
Map shows transect stationsand depth contours
Dissolved Inorganic –nitrate, nitrite, phosphate, ammonium, silicate
X
Particulate C, N, P X XTotal Dissolved N, PTotal N, P
X
Dissolved organic carbon XTotal Suspended solids XBiogenic silica XChlorophyll a X XPAR, secchi depth, attenuation X
Dissolved oxygen XT, S, turbidity, transmissivity XPhytoplankton taxonomy XGrain size, benthic taxonomy XTotal organic matter/organic C XBulk density, porosity, % water X
Primary productivity (14C & FRRF) X
Bacterial productivity (3H-Leucine)
X
Respiration rates XSediment oxygen demand XSulfate reduction rates XBenthic nutrient flux X
Parameter Water SedimentGulf Hypoxia Monitoring Data – discrete waters samples collected at minimum of 2 and maximum of 6 depths depending on water column structure and depth
93° W 92° W 91° W 90° W
28° N
29° N
30° N
0
2
4
6
8
10
kg/m3
June 9 – 19, 2003
Water column stratificationand Hypoxic Region
93° W 92° W 91° W 90° W
28° N
29° N
30° N
0
1
2
3
4
5
6
7
8
9
10
µg/L
June 9 – 19, 2003
Surface Chlorophyll aand Hypoxic Region
93° W 92° W 91° W 90° W 89° W
28° N
29° N
30° N
Bottom Dissolved Oxygen (mg/l)LA Shelf / Gulf of Mexico -- 3/22 - 3/31/2005
9 3 9 2 9 1 9 0 8 9
2 8
2 9
3 0
R e l a t i v e C h l o r o p h y l l - a F l u o r e s c e n c eL A S h e l f / G u l f o f M e x i c o - - 3 / 2 2 - 3 / 3 1 / 2 0 0 5
- 8
- 4
0
4
8
1 2
1 6
2 0
+ + + + + S h i p T r a c k
Resolving Seaward Boundary Conditions
Resolving Seaward Boundary Conditions
Salinity distributions along transect D showing oceanic conditions seaward
Dep
th (
m)
0 2 0 4 0 6 0 8 0 1 0 01 4 0
1 2 0
1 0 0
8 0
6 0
4 0
2 0
0
June 2003
Transect Distance (km)0 1 0 2 0 3 0 4 0 5 0 6 0 7 0 8 0 9 0 1 0 0
1 4 0
1 2 0
1 0 0
8 0
6 0
4 0
2 0
0
March 2003
-9 0.5 -9 0.4 -9 0.3 -9 0.2 -9 0.1 -90 -8 9.9 -8 9.8 -8 9.7 -8 9.6 -8 9.5 -8 9.4 -8 9.3 -8 9.2 -8 9.1 -89
29
2 9.2
2 9.4
Time
09:00:00 11:00:00 13:00:00 15:00:00
Sal
inity
0
5
10
15
20
25
30
PO
43
- ( M
)
0.0
0.5
1.0
1.5
2.0
Salinity
0 5 10 15 20 25
PO
43- ( M
)0
1
Continuous Surface Mapping Array MS River to Continuous Surface Mapping Array MS River to FourchonFourchon
Surface salinity and PO43-
Cruise trackStart
Stop
Mixing zone
Not baseline corrected
Project TimelinesProject Timelines
FY ‘02 FY ‘03 FY ‘07FY ‘06FY ‘05FY ‘04
Planning
Field Monitoring
Sample/Data Analysis
Database Development
Model Development& Application APM APM APM
Cruise WQ DbaseReport Trends
FY ‘08