East Harbor: Difference between revisions
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[[Image:EastHarbor_InletLocations.jpg|thumb|right|500px|Figure 1. East Harbor, Massachusetts, Historical inlet location (a, left) and present-day culvert opening (b, right) (USACE, 1868; MassGIS, 2003) .]] | [[Image:EastHarbor_InletLocations.jpg|thumb|right|500px|Figure 1. East Harbor, Massachusetts, Historical inlet location (a, left) and present-day culvert opening (b, right) (USACE, 1868; MassGIS, 2003) .]] | ||
East Harbor is an example of a tidally-restricted estuary located north of Truro, Massachusetts, on Cape Cod. The system consists of three main components; Pilgrim Lake, Moon Pond and Salt | East Harbor is an example of a tidally-restricted estuary located north of Truro, Massachusetts, on Cape Cod. The system consists of three main components; Pilgrim Lake, Moon Pond and Salt Meadow. The study will focus on restoring tidal exchange between Cape Cod Bay and Pilgrim Lake/Moon Pond components. The Harbor is connected to Cape Cod Bay by a 2.2 m<sup>2</sup> area by 200-m long culvert leading to a poorly flushed marsh area which in turn empties into a lake and marsh system. The original inlet located at the north end of the estuary (Figure 1a) was closed by the construction of a dike in 1869. The motivation behind this closure was to reduce or eliminate the erosion occurring on the seaward side of East Harbor and later provided railroad access to Provincetown (USACE, 1868; NOAA, 2006) Tidal access to the estuary was relocated at the southern end of the estuary with a fixed culvert with dimensions 1.1 m by 2 m (Figure 1b). This closure significantly changed hydrodynamics of the system and sediment transport on Cape Cod Bay and within the estuary. | ||
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== Project Objectives == | == Project Objectives == | ||
The goal of this study is to evaluate alternatives for increasing the tidal range in East Harbor, which will improve tidal flushing and water quality. The CMS model will be used to determine not only the effect a variety of inlet configurations will have on the system in terms of flushing and habitat restoration but also examine the nearshore response. Preliminary analysis of the site using a 1D Escoffier – Inlet Equilibrium model (CEA; Seabergh and Kraus ) indicated the stable equilibrium for a natural inlet reopened at the site is approximately 340 | The goal of this study is to evaluate alternatives for increasing the tidal range in East Harbor, which will improve tidal flushing and water quality. The CMS model will be used to determine not only the effect a variety of inlet configurations will have on the system in terms of flushing and habitat restoration but also examine the nearshore response. Preliminary analysis of the site using a 1D Escoffier – Inlet Equilibrium model (CEA; Seabergh and Kraus ) indicated the stable equilibrium for a natural inlet reopened at the site is approximately 340 m<sup>2</sup>, and the minimum cross-section is 10 m<sup>2</sup>. However, the present land ownership limitations at the site are a maximum width of 23 m. | ||
Latest revision as of 14:50, 1 December 2010
UNDER CONSTRUCTION
East Harbor is an example of a tidally-restricted estuary located north of Truro, Massachusetts, on Cape Cod. The system consists of three main components; Pilgrim Lake, Moon Pond and Salt Meadow. The study will focus on restoring tidal exchange between Cape Cod Bay and Pilgrim Lake/Moon Pond components. The Harbor is connected to Cape Cod Bay by a 2.2 m2 area by 200-m long culvert leading to a poorly flushed marsh area which in turn empties into a lake and marsh system. The original inlet located at the north end of the estuary (Figure 1a) was closed by the construction of a dike in 1869. The motivation behind this closure was to reduce or eliminate the erosion occurring on the seaward side of East Harbor and later provided railroad access to Provincetown (USACE, 1868; NOAA, 2006) Tidal access to the estuary was relocated at the southern end of the estuary with a fixed culvert with dimensions 1.1 m by 2 m (Figure 1b). This closure significantly changed hydrodynamics of the system and sediment transport on Cape Cod Bay and within the estuary.
Project Objectives
The goal of this study is to evaluate alternatives for increasing the tidal range in East Harbor, which will improve tidal flushing and water quality. The CMS model will be used to determine not only the effect a variety of inlet configurations will have on the system in terms of flushing and habitat restoration but also examine the nearshore response. Preliminary analysis of the site using a 1D Escoffier – Inlet Equilibrium model (CEA; Seabergh and Kraus ) indicated the stable equilibrium for a natural inlet reopened at the site is approximately 340 m2, and the minimum cross-section is 10 m2. However, the present land ownership limitations at the site are a maximum width of 23 m.
Questions to be answered by the CMS Modeling study:
- How big does the inlet need to be to stay open/stable?
- What is the appropriate inlet location and size?
- What is the worst case volume of sand would need to be bypassed?
- What are the likely dimensions of potential structures?
Model Setup
Model Forcing
Since field data in the area is extremely limited, the flow model will be driven with water surface elevation data from the ADCIRC tidal database in combination with an adjusted tide from Boston tide gauge. Harmonic analysis and observation between a limited field data collection between Provincetown (located on the inside of the Cape Cod Hook) and Boston reveals a small amplitude and phase offset. No existing wave data has been identified so all wave generation is performed through the CMS-Wave model from wind wave generation.
Grid Configuration
Since the existing culvert dimensions are 1.1 m x 2 m oval concrete pipe, the telescoping grid will allow for very small grid cell size (0.5 m) while maintaining reasonable computational run time.
Table XX. Sediment transport and morphology parameters in the CMS
Parameter | Value |
---|---|
Formulation | |
Sediment Transport Formula | |
Bed Load Scaling Factor | |
Suspended Load Scaling Factor | |
Sediment Porosity | |
Bed Slope Coefficient | |
Morphologic Acceleration Factor | |
Total Load Adaptation Length Method | |
Adaptation Length |
Model Calibration
Since field data is extremely limited in this area, model calibration will be using a limited set of field data collected in 2005 from a previous study. This includes water surface elevation from Provincetown Harbor, the Moon Pond end of the culvert, and Pilgrim Lake. Morphology calibration is not possible due to lack of available repeated bathymetric surveys.
Discussion
- For a definition of the goodness of fit statistics see Goodness of fit statistics
References
- Seabergh, W.C., and Kraus, N.C. (1997). “PC program for coastal inlet stability analysis using Escoffier method,” Coastal Engineering Technical Note CETN IV-11, U.S. Army Engineer Research and Development Center, Vicksburg, MS, 7 p
- Headquarters, U.S. Army Corps of Engineers. (1868). “Provincetown Harbor, Massachusetts.” Annual Report of the Secretary of War: Appendix RS, 828-829.
- Watts, I. M., Rosati, J. D., Borelli, M. (2010) "Re-Establishing a Historical Inlet at East Harbor, Cape Cod" Coastal Sediments '11 Conference Proceedings, In Press