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A Shallow-water Coastal Habitat Model for Regional Scale Evaluation of Management Decisions in the Chesapeake Region C. L. Gallegos, D. E. Weller, T. E.

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Presentation on theme: "A Shallow-water Coastal Habitat Model for Regional Scale Evaluation of Management Decisions in the Chesapeake Region C. L. Gallegos, D. E. Weller, T. E."— Presentation transcript:

1 A Shallow-water Coastal Habitat Model for Regional Scale Evaluation of Management Decisions in the Chesapeake Region C. L. Gallegos, D. E. Weller, T. E. Jordan, P. J. Neale, J. P. Megonigal RD-8308701-0

2 Overview Study Systems Stressors of Interest Objectives and Tasks Modeling Approach Model Structure Users, Products, and Progress

3 Importance of Shallow-water Tributary Embayments (STE) in Chesapeake Bay Formation of estuaries as drowned river mouths has resulted in highly articulated shorelines for east coast estuaries.

4 Shallow-water Tributary Embayments are Critical to Two of the Designated Use Categories

5 Susceptible to Large Phytoplankton Blooms due to Shallow Water and Proximity to Nutrient Sources Rhode River, MD Continuous Monitor April 16-30, 2004

6 High Phytoplankton Productivity Results in Low A.M. D.O. and Large Diurnal Swings MD Department of Natural Resources, “Eyes on the Bay”, Shallow Water Monitoring Program, Rhode River 2004. http://mddnr.chesapeakebay.net/newmontech/cont mon/eotb_results_graphs.cfm?station=SERC

7 Catastrophic Losses of SAV in Chesapeake Bay Occurred First in Western Shore STE July 1966July 1967 Distribution of Water Milfoil in the Rhode River, MD Bayley, S., H. Rabin and C. H. Southwick, 1968. Recent decline in the distribution and abundance of Eurasian milfoil in Chesapeake Bay. Chesapeake Science 9: 173-181.

8 Areas Slated for Restoration of SAV are Concentrated in Shallow Tributary Embayments and Tidal Creeks Chesapeake Bay Program Tier-II Restoration Goal: Restore SAV to the 1-m contour in areas in which it historically occurred.

9 Main CB Model Segmentation Scheme Treats Most STE as 1 to 3 Cells West R. Rhode R. South R. Severn R. Magothy R.

10 Premise: The ecological importance of shallow-water tributary embayments far exceeds their volumetric contribution to the Bay, and the main-stem concentrations of water quality constituents.

11 Global Change-related Stressors of Interest Atmospheric CO 2 Concentrations rose by 30% in 20th century, and continuing to rise at ca. 1% per year. Altered growth rates of emergent vegetation Uncertain effects on export of carbon from wetlands Uncertain effects on seasonally average temperatures Uncertain effects on rainfall and runoff patterns Potential Impacts on Shallow Tributary Embayments

12 Global Change-related Stressors of Interest Elevated UV Radiation Incident UV-B has increased ca. 1.3% per year since the mid-70’s (Neale et al. 1999). Despite strong attenuation by CDOM, UV inhibits phytoplankton production by ca. 50% at the surface, with average of 15% inhibition over a 1.5 m water column (Neale 2001).

13 Land-use/Climate Change Interactions Global Change-related Stressors of Interest Despite uncertainty in global temperature change, increased frequency of droughts and flashier flow regimes are considered likely Altered flow regimes and changes in land use patterns will have consequences for the delivery of nutrients and sediments to estuaries

14 Objectives and Tasks: Estuarine Modeling End Points Objective: To provide a tool to predict the magnitude and trends of existing and emerging indicators of the ecological condition of critical shallow water habitats. Important Stressors: Suspended Sediments Nutrients UV Irradiance Model Output: Phytoplankton Chlorophyll Water Clarity (diffuse attenuation coefficient) Dissolved Oxygen

15 Questions of Interest How do nutrients and suspend sediments interact to determine the growth of phytoplankton under altered land-use and climate regimes? How will concentrations of CDOM respond to changes in land use (e.g. wetland coverage) or in situ eutrophication, and what are the implications for penetration of UV radiation?

16 Use spatial analysis to describe the “population” of STE around the shore of Chesapeake Bay and its major tributaries Apply previously developed statistical models relating land cover and physiographic province to nutrient discharges to quantify the distributions of local watershed inputs of water and nutrients across the population of STE Objectives and Tasks: Watershed Inputs to STE

17 Objectives and Tasks: Carbon Export from Wetlands How does export of DOC from wetlands depend on concentration of atmospheric CO 2 ? How does export of CDOM vary among physiographic province and land cover?

18 Modeling Approach STE exhibit a wide range of sizes, shapes, influence by local watershed, and exchange with main stem estuary STE are far too numerous to model individually, on a creek- by-creek basis

19 Modeling Approach We will employ an approach that uses a large number of simple, generic models of subestuaries and tidal creeks, incorporating inputs from local watersheds, internal processing, and exchange at the seaward boundaries Our approach will make extensive use of Monte Carlo simulation and generalized sensitivity analysis to determine a range of outcomes, under different management scenarios, for the diversity of shallow- water systems encountered around Chesapeake Bay.

20 Model Structure: Conceptual We conceive of STE as part of a continuum of aquatic ecosystems linking watersheds with coastal marine waters Focus on well-mixed estuarine tidal waters, which contain a mixture of freshwater from their local watershed, and more saline water from adjacent estuarine or coastal waters

21 Model Structure: Stressor Interactions Ecosystem Component Stressor Interactions Within-Component Response Variable: Stressor Delivery to- or Response within- Estuary WatershedLand-use × Climate-related flow alteration Nutrients, sediment, and CDOM Wetlands and Marshes Rising CO 2 × Changing wetlands distribution Below-ground CDOM flux EstuaryNutrients, sediment, & CDOM × Rising UV Phytoplankton chlorophyll Water clarity Dissolved oxygen Important stressors vary in different component ecosystems in the landscape Response variables in watersheds and wetlands are sources of stressor inputs to STE Response variables within STE are the indicators being used to evaluate management success

22 Model Structure: Flow Endpoints

23 Products and Users Cumulative distribution functions of indicators being used for assessment of CWA compliance Chesapeake Bay Program State agencies Tributary strategy teams Watershed planners

24 Progress

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