WRIG - Community Stakeholder Consultations 16/03/2011
Estuaries in PEI Why are some more susceptible to nutrient loads - - PowerPoint PPT Presentation
Estuaries in PEI Why are some more susceptible to nutrient loads - - PowerPoint PPT Presentation
Estuaries in PEI Why are some more susceptible to nutrient loads than others? 1 WRIG - Community Stakeholder Consultations 16/03/2011 Nutrient Susceptibility It has been apparent for Oyster mortality some time that each estuary
WRIG - Community Stakeholder Consultations 16/03/2011
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Nutrient Susceptibility
It has been apparent for
some time that each estuary in PEI has a specific load that it can tolerate
Some have re-occurring
anoxia and “small” loads
Some have little or no
anoxia despite high loads
Something in the estuary
itself is driving this
Biological/Chemical Physical
Oyster mortality following anoxic event – Southwest River, PEI. July 2006
WRIG - Community Stakeholder Consultations 16/03/2011
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Island Estuaries with Re-Occurring Anoxic Events 2002 - 2010
>6 Anoxic Events 3-6 Anoxic Events 1-2 Anoxic Events
Number of Estuaries with Recorded Anoxic Events (2002 - 2010) PEI 5 10 15 20 25 2002 2003 2004 2005 2006 2007 2008 2009 2010 Year Number> 6 anoxic events 3-6 anoxic events 1-2 anoxic events
WRIG - Community Stakeholder Consultations 16/03/2011
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WRIG - Community Stakeholder Consultations 16/03/2011
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Nutrient Target Setting for PEI Estuaries
Ambient tidal ranges appeared to be driving much of
the susceptibility to nutrients in PEI estuaries
A very simple model developed (Gary Bugden, DFO-
BIO Estuary Load FW Volume + SW Volume
Model appears to work for most estuaries on PEI
WRIG - Community Stakeholder Consultations 16/03/2011
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Results
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40
BDR BRA BRE BRR BWR CAB CAS COL COV ENM FLA FRE GDR HBR IND KIL MGR MIR MOR MUR NLB NLC NOR ORB PIN RUS SPB SSH SWR TRB TRY WES WIL WIN
Estuary Delta-N (mg/l) Anoxia Not Reported Anoxia Reported
0.06 mg/l 0.10 mg/l
Critical N Range
WRIG - Community Stakeholder Consultations 16/03/2011
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Issue - Tidal Flushing
Causeways and Bridges
–
Many of them date from the 50’s and 60’s
–
Small openings easier and cheaper to build
–
Not always engineered for a full opening
lack of planning
- ther reasons (freshwater impoundments)
WRIG - Community Stakeholder Consultations 16/03/2011
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Wheatley River Has A Bridge!
Was constructed ~1972. There was also a bridge there prior to that. Bridge is in good shape.
Opening (gap) is 20m. Effective water depth is 1.7 m (was 1.3 m)
Studied in 2009 for TIF, (Mark MacNeil)
Results
–
No sill present
–
Admitted 95% of the tide (all but the highest tides)
–
Restriction due to the bridge channel and not downstream or upstream shoal area
–
Debris from previous structure present. Removal
- f debris recommended increasing depth under
bridge by 0.4 m and restoring 100% of tide.
–
Tidal currents under the bridge have decreased slightly as a result.
–
Work has been carried out (2009)
From MacNeil. 2009
WRIG - Community Stakeholder Consultations 16/03/2011
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Wheatley River Tidal Ranges
- 0.6
- 0.4
- 0.2
0.2 0.4 0.6 0.8 1 30/06/2009 04/07/2009 08/07/2009 12/07/2009 16/07/2009 20/07/2009 24/07/2009 28/07/2009 01/08/2009 Date Tide Height (m) Hunter River Rustico Bay Above Oyster Bed Bridge
WRIG - Community Stakeholder Consultations 16/03/2011
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Wheatley River Tidal Ranges
- 0.6
- 0.4
- 0.2
0.2 0.4 0.6 0.8 1 03/07/2009 07/07/2009 11/07/2009 Date Tide Height (m) Hunter River Rustico Bay Above Oyster Bed Bridge
WRIG - Community Stakeholder Consultations 16/03/2011
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Vernon River Restricted Tide Heights
below causeway above causeway
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Other Studies
1986 “A Study of Water Quality Issues at Selected Prince
Edward Island Causeways” For PEI Department of Transportation and Public Works (P. Lane and Jacques Whitford)
1996. “Numerical Modelling of Rustico Inlet, PEI” for Parks
Canada (Baird and Associates)
1998. “Computer Modelling of Rustico Bay Hydrodynamics” for
Parks Canada (Baird and Associates)
1998. “Assessment of Potential Water Quality Impacts
Resulting from Removal of Rustic Island Causeway”. For Parks Canada (Mike Brylinsky)
WRIG - Community Stakeholder Consultations 16/03/2011
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Other Physical Factors in Estuary Susceptibility
Residence time
–
How long does it take a molecule of water entering at the upper end to exit the lower?
Bathymetry
–
Relative size of photic zone
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Presence of stratification
Size/Shape
–
Are there tidal flats?
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Long and skinny may force water in rather than out
Orientation
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Prevailing wind direction
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Movement of sediments/sand
Presence of Sills
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Upstream Stagnation
WRIG - Community Stakeholder Consultations 16/03/2011