Chesapeake Bay Program Modeling Subcommittee Quarterly Review and Joint Meeting with the Sediment Workgroup Chesapeake Bay Program Office; Annapolis, MD July 2, 2008 MEETING SUMMARY Meeting Materials Meeting Website: http://archive.chesapeakebav.net/calendar.cfm?eventdetails=9048 Agenda 7-2-08 Chesapeake Modeling Symposium - Presentation by Kevin Sellner Overview of WQSTM Objectives for the Clarity Simulation - Presentation by Carl Cerco Foundations of the Suspended Solids Model - Presentation by Carl Cerco Characteristics of Sediment Transport Module for CBP WOM - Presentation by Sung-Chan Kim Refining the Calibration of WQSTM for Simulation of the Claritv/SAY Water Quality Standard- Presentation by Carl Cerco Shallow Water Monitoring - Presentation by Carl Cerco Attachment A: Initial Scoping Scenarios for the Water Quality and Sediment Transport Model's Assessment of the Claritv/SAY Water Quality Standard SAY Application - Presentation by Carl Cerco Phase 5.1 Progress DRAFT Response of the Modeling Subcommittee to the Second STAC Review of the Phase 5 Community Watershed Model (July 1, 2008) Comments on CBPO Draft Response to STAC Phase 5 Review I. Announcements and Amendments to the Agenda Linker Lewis Linker, Modeling Subcommittee Chair and Sediment Workgroup Coordinator, began the meeting at 9:00 am. Introductions were made and the meeting's agenda was reviewed. II. Chesapeake Modeling Symposium 2008 Sellner Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 1 9048.pdf Kevin Sellner, CRC, described the outcomes of the Chesapeake Community Modeling Program's (CCMP) May 12-14 Chesapeake Modeling Symposium. This symposium showcased existing Chesapeake modeling efforts and promoted information exchange and open modeling in the region. This symposium was a venue to: o Promote information exchange and open modeling in an attempt to stimulate cross-pollination across modeling teams and paradigms o Identify and showcase existing modeling efforts o Encourage future community modeling and data sharing 1 ------- o Present the latest CCMP progress o Encourage more bottom-up interaction between CCMP and the community o Facilitate the development of an inventory of models and data sets, and stimulate collaborative research on data processing and modeling The 3-day symposium included 9 workshops, 7 plenary talks, 27 break out discussion sessions, and over 70 presentations and papers (which are available for download at the following website: http://www.chesapeakemeetings.com/CheMS20Q8/web- sessions.php). A product of the symposium was the Chesapeake Bay Basin Assets diagram (see slide 13). This diagram identifies data sets, models, and products. Let CCMP know if there is something that you think needs to be added to this diagram. CCMP will hold modeling symposiums every two years. CRC is holding a regional conference in March 2009 on ecosystem-based management. Modeling sessions can be included in this conference. III. Overview of WQSTM Objectives for the Clarity Simulation Cerco Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 2 9048.pdf Carl Cerco provided an overview of the WQSTM objectives for the sediment simulation for assessment of the shallow water clarity water quality standard. A lot of issues were raised after the completion of the last version of the model (13,000 cell). These issues included: o Absence of sediment resuspension o Bank loads (magnitude, below sea level, periodicity) o Light attenuation (partial absorption model, parameter evaluation) Following are a list of actions that have been taken to help remedy these issues in the new version of the model: Sediment Resuspension o Net settling of fixed solids was replaced with dynamic settling and resuspension. o Solids classes were increased from one to four, o Resuspension is now driven by shear stress from waves and currents. Bank Loads o A state-of-the-art detailed spatial estimate was completed by Halka and Hopkins. o Below-sea-level erosion as a fraction of above sea level, o The timing is related to local daily wave energy and storm surge. Light Attenuation o The partial absorption model has been replaced with an advanced optical model. o It accounts for scattering and absorption by solids and color, o It is parameterized spatially and temporally, as far as possible, by observations. IV. Foundations of the Sediment Transport Model Cerco/Kim Carl Cerco and Sung-Chan Kim reviewed the model structure, state variables, bed model, and forcing functions. 2 ------- Carl Cerco Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 3 9048.pdf Suspended Solids Model o The suspended solids model operates on a 57,000 cell grid, o Shear stress from currents is generated by the CH3D hydro model, o Shear stress from waves is from the independent wave model, o Solids calculations are conducted in the water quality model, o There are four non-cohesive sediment classes: fine clay, clay, silt, and sand, o Assumptions include: no coagulation; no bedload; distributed load splits from the Watershed Model; and bankload splits recommended by originators ROMS Bed Model o The ROMS Bed Model includes seven layers that are initially 1 cm thick. The number of layers and layer thickness do not change, o No erosion or deposition through the bottom of the bed. o No provision to change critical shear stress as a function of depth into sediments or material age. o The bed will armor. Erosion of clays and silt leaves sand behind. SAV Feedback Effects o Computed SAV reduces computed bottom shear stress, o Reduction is proportional to fraction of cell depth occupied by SAV. Sung-Chan Kim Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 4 9048.pdf Sung-Chan showed the group graphs depicting wave height and period at three different Bay stations (Calvert Cliffs, Mid Bay, Poplar Island), he explained how the BBL model estimates bottom shear stress, and he shared animations for a large flooding event in January 1996 and for a whole year in the mid-Bay and lower-Bay. Summary: o Young and Verhagen's (1996) depth-limited fetch-limited parametric wave model gives reasonable wave heights and periods especially in the Upper and Mid Bay. o The bottom boundary layer model (Harris) estimates bottom stresses resolving spatial and temporal (tidal and subtidal) variations, o Upper Bay ETM varies with tidal and event scales. o Cross-Bay sediment concentrations vary with corresponding bottom stresses (as well as advection). V. Sediment Simulation Progress Since the April 2008 Quarterly Cerco Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 5 9048.pdf Carl Cerco presented the progress that has been made on refining the calibration of the Water Quality and Sediment Transport Model (WQSTM) for the simulation of the clarity/SAV water quality standard. Carl's summary points and recommendations: o The model represents the general behavior and distribution of suspended solids and light attenuation in the bay and most major tributaries. 3 ------- o Improved representation of suspended solids and light attenuation, especially along the bay axis, is desirable, o We have been applying a universal set of model parameters (settling velocity, etc.). Improvements by following this path are unlikely. The best hope, right now, is in spatially varying settling velocities, o We can continue this process indefinitely. o Our strongest recommendation is to apply the model as it exists in sensitivity analyses and screening scenarios. Implement improvements as model behaviors become apparent. Comments: o We should look into whether or not we have the salinity right in the Patuxent. This may help us determine how to tune the settling velocity, o Getting the light attenuation correct is important for the SAV standard. Carl said that they will attempt to improve the solids in the limited amount of time that they have. However, we may just need to recognize and take into account that the light attenuation model has some gaps in it. o The turbidity max was missing in the lower Bay. o For KE, we again had a step function. o All adjustments that are made should be locked so that they don't have to be made again when scenario runs are performed, o It is important to get the boundary conditions right in the shallow water area, o It is probably not a good idea to adjust the mechanics spatially, which is what you would be doing if you vary the parameter spatially. This hides hints that the model is doing something wrong, o Rather than varying the parameter spatially, one option may be to add another size class. This would allow the settling velocity to be altered in a way that corresponds to a change in size class. However, this may be difficult since we are data limited. o Since we only have six weeks left until we need to provide this model, a compromise may be to improve the boundary conditions while at the same time recognizing that there is a failure in the model's current structure of inputs in certain areas (such as the lower turbidity max), o Rather than adjusting the fundamentals of the model to correct KD, one option may be to take the difference between what is observed and what is predicted and apply that as something like a correction factor. ACTION: In the six weeks that are remaining, Carl agreed to take another look at the solids and potentially adjust the light attenuation model. VI. Simulation of Shallow Water SAV/Clarity Water Quality Standard Cerco Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 6 9048.pdf The Modeling Subcommittee reviewed information regarding the shallow water simulation, including sediment resuspension, refined shore erosion estimates, and the SAV simulation. An emphasis was placed on the calibration of the SAV acres, observed and simulated, in the different Chesapeake Bay segments. Carl's summary points and recommendations: o With few exceptions, the differences (computed and observed) between deep and shallow-water attenuation are small, just a few tenths of a unit. 4 ------- o The computed components of attenuation are site-specific, o There is, perhaps, a tendency for clays to be more significant at deep stations and less significant at shallow stations, o It will likely take an extensive series of sensitivity runs to sort this out: ฆ Eliminate distributed loads ฆ Eliminate bank loads ฆ Eliminate open boundary conditions ฆ Eliminate SAV feedback effects Comments: o Eliminating resuspension should potentially be added to this list, o We need to understand why we are getting the results that we are getting, o There is no sediment size information in the standard shallow water monitoring program. VII. Initial Scoping Scenarios Linker Handout: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Handout 1 9048.pdf The Modeling Subcommittee reviewed and discussed the proposed initial scoping scenarios for the WQSTM's assessment of the clarity/SAV water quality standard (see handout). Comments on the handout: o A scenario that eliminates resuspension loads should be added, o A scenario that sets the ocean boundary to zero should be added, o For the sediment response scenarios, if you turn off the watershed inputs, how much of a spin-up do you need? Is a ten year spin-up adequate? ฆ The model may need to be run until equilibrium is reached. If this is more than ten years, how many more years are needed? ฆ Since there are so many possible scoping scenarios, one option may be to run each of them for a relatively short period of time in order to narrow down the choices as to which ones should be run longer. o A scoping scenario that looks at the influence of direct drainage above or below the fall line could be useful for the TMDL. Timeline o July 17th: Review and approval of the initial scoping scenario plans by the Reevaluation Technical Workgroup o July 21st: Review and approval of the initial scoping scenario plans by the Water Quality Steering Committee o August 18th: Initiate first scoping scenarios o October 7th-8th: Completion of key initial scoping scenarios prior to the Oct. 7th-8th MDSC/SedWG Meeting o October: Presentation of the key initial scoping scenarios to the Water Quality Steering Committee at their October meeting date The Sediment Workgroup will also be helping to develop a maximum feasible sediment reduction scenario. This scenario should be completed in January 2009. The Modeling Subcommittee will have time to review the scoping scenarios before they go to the Water Quality Steering Committee. 5 ------- ACTION: Lewis will revise the handout based on today's comments and will send it out to Modeling Subcommittee members for review. DECISION: The Modeling Subcommittee had no objections to moving forward with the initial scoping scenario plan as revised at today's meeting. VIII. Simulation of Shallow Water SAV/Clarity WQ Standard (Cont.) Cerco Presentation: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Presentation 7 9048.pdf Initial conditions: How do we initialize the model? Every cell and depth increment? Without population processes, do initial conditions matter? SAV areas: What is the appropriate area in which to allow SAV to grow? If we allow all area within the 2 m contour we get way too much SAV. Is the process deterministic? Other processes: Should we consider local mortality (e.g., from wave action)? Vary the ratio of detrital epiphytic material to viable epiphytes? Carl's summary points, conclusions, and recommendations: o The SAV unit model is reasonably well calibrated. SAV responds as expected to changes in light attenuation, o Can anyone with GIS skills help to establish initial conditions for SAV? o We suspect the changes in light attenuation over 7 years are too small to promote significant trends in SAV. We need to do two things: ฆ Shock the model with major changes in light attenuation. Examine SAV response. ฆ Validate the model to long term data when the 20-year model runs are executed. Carl will start to gather biomass information. A full 20-year run should be initiated as soon as the code is completed in mid-August. How much is the biomass feedback effect contributing to this overestimation? This would be interesting to look at. IX. Comments from the Sediment Transport Model Review Team The Sediment Transport Model Review Team provided their initial response to the questions listed in today's agenda. They will provide written responses at a later date. Chris Sherwood The model is vastly improved. It has more physics and more processes incorporated into it, which will make it a better model for its intent. Some of the simulations that Sung-Chan presented today, such as how the model reacts to an event, were simulations that Chris had been looking forward to seeing for some time. He didn't get much of a sense of how the model responds to changing parameters (e.g., settling velocity). It is beneficial to document how the model changes when adjustments are made. The component of the model that he has the biggest reservations about is the light model. It would be nice if this component incorporated size and if it didn't have spatial variation. 6 ------- Rather than introducing spatial variation, it may be possible to instead introduce another state variable to help address these issues. The model has a lot of the important structures that it needs to effectively simulate shallow water light attenuation in the shallow water areas of the Chesapeake. The model's improved shore erosion, resuspension, watershed inputs and estuarine boundary conditions should help result in more accurate model responses. The sediment transport model seems to be doing the right thing. It would be interesting to see how sediment inertia affects this. From his point of view, it seems that the SAV model is running well. However, this is not his area of expertise. For the next generation of the model, the same types of improvements should continue to be made (such as adding physical processes and trying to more accurately capture what is actually going on in the real world). The sensitivity analysis and the scenario testing should reveal a lot about how the model responds. Allen Teeter In general, the sediment transport model seems to be reproducing the general characteristics of sediment transport in the Bay. With respect to shoreline erosion, is the model forming a sand layer where the sediment is being deposited? Sung-Chan said that he would check to see if this is happening. He liked Sung-Chan's vertical comparison of shallow water sites. Further sensitivity tests on the erosion parameters and the settling parameters would be helpful. Perhaps adjusting the erodibility parameter would be more justifiable in a spatial sense than adjusting the settling parameter. For the next generation of the model, it would be useful to: o Add more processes o Potentially adjust the settling rates o Incorporate some linear varying bed properties in the bed model so that there aren't jumps when the layers change o Vary erodibility with depth through some consolidation or hardening of the bed o Possibly add several more grain classes Larry Sanford The model has come a long way and overall is looking pretty good. The fact that the processes are behaving as they should is a big leap forward. If you are going to tinker with it to make it agree better, tinker with something at the end rather than something in the middle such as a basic mechanism. It may be helpful to readjust the settling speeds so that they are more evenly distributed. There is a huge gap between the current settling parameters (specifically between clay and silt). 7 ------- If he were going to adjust the settling speeds, the metric that he would look for would be more of a clearing in slack water. For the future, another feedback for SAV may be to adjust it by the bottom sediment type, if that information is available. Could we make the organic carbon behave like a sediment particle in the model? He agreed with Allen that moving towards implementing flocculation in some format may help to address some of the spatial issues such as the sharpness of the turbidity maximum. The Modeling Subcommittee thanked the review team for their comments and invited them to continue to participate in future Modeling Subcommittee meetings. X. Status of the Phase 5.1 Model Shenk Handout: http://archive.chesapeakebav.net/pubs/calendar/MODSC 07-02-08 Handout 2 9048.pdf See the handout for an update on the status of the Phase 5.1 model, which includes information on the data and processes that have been revised. Phase 5.1 will be completed and linked to the Water Quality and Sediment Transport Model in mid-August. XI. Response to the 2nd Phase 5 Review Linker Modeling Subcommittee members reviewed the July 1st draft of the Modeling Subcommittee's response to the second STAC review of the Phase 5 Community Watershed Model, as well as the comments that were received. Lewis received comments from many of the Modeling Subcommittee members during the early-June comment period. These comments will be incorporated into the Modeling Subcommittee's final response. XII. Adjourn The meeting was adjourned at 2:00 pm. Participants Steve Bieber COG sbieber(fl),mwcos.ors Sally Bradley CRC/CBP sbradlevฎ,chesapeakebav.net Carl Cerco US Army ERDC carl. f. cerco(o>,usace. armv .mil Monir Chowdhury DC DOE monir. chowdhurv(ซ),dc. sov Lee Currey MDE lcurrev(ซ),mde. state, md. us Bill Keeling VADCR william.keelinsfaidcr. virsinia.sov Sung-Chan Kim US Army ERDC suns-chan.kimffl),usace.armv.mil Lewis Linker EPA/CBP 1 inker, lewisฎ epa.yov Ross Mandel ICPRB rmandel(o>,icDrb.ors Kevin Sellner CRC/STAC sellnerkฎ si.edu Gary Shenk EPA/CBP sshenkfo),chesaoeakebav.net Chris Sherwood USGS csherwood(o>,usss. sov Rou Shi MDE rshi(o),mde. state.md.us Allen Teeter CHT cht alienฎ,canuflv.net 8 ------- Harry Wang Ping Wang VZMS UMCES/CBP hvwang@vims.edu pwang@chesapeakebav.net On the phone: Kenn Pattison Larry Sanford PA DEP UMCES kpattison@state.pa.us 1 sanford@hpl. umce s. edu 9 ------- |