OKANAGAN TENNANT & WUW METHODS · 2019. 1. 15. · Okanagan Tennant Method Progress to date • We...
Transcript of OKANAGAN TENNANT & WUW METHODS · 2019. 1. 15. · Okanagan Tennant Method Progress to date • We...
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OKANAGAN TENNANT & WUW METHODS
EFN conferenceOctober 2018
Vaseux Creek
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EFN StudyStudy design plans in 2016
• Phase 1 - AE developed the methods document
• All sampling and analysis is done following the methods set out in the 2016 AE methods document
• ONA gathered and developed HSI indices for WUW work with Ron Ptolemy
• Defensible, transparent and robust EFN values for Okanagan tributaries
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Okanagan Ecosystem InitiativeEnvironment and Climate Change Canada study
• Concurrently ONA studied biological response and EFN assessments by
• Comparing benthic macroinvertebrate communities to hydro-modification, riparian function and flow issues
• Includes habitat mapping of 6 north Okanagan streams and CABIN based assessments of reaches
• Outcomes could be an additional source of information for the EFN methods
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EFN StudyStudy implementation starting in 2017
• ONA created the HSI curve for spawning Sockeye Salmon depth and velocity.
• Completed SEFA analyses for WUW work with Ryan Whitehouse (MoFLNRO) to test as a possible method
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Depth (m)
Depth
Proposed HSI
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Velocity (m/s)
Velocity
Sockeye Velocity
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Study implementation starting in 2017
• Study tributaries were selected based on criteria
- Low flow issues
- No EFNs presently
- # water license applications
- Habitat value
- Potential for restoration
- Overlap with other projects
EFN Study
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1. Coldstream2. Lower Vernon3. Equesis4. Naswhito5. Whiteman6. Kelowna (Mill)7. Mission8. Powers9. McDougall10. Trepanier11. Naramata12. Shorts13. Penticton14. Trout15. McLean16. Shuttleworth17. Shingle18. Inkaneep19. Vaseux
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EFN Study
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• Phase I – methods selected include• Okanagan Modified Tennant Method
• Desktop method using available information• Low-risk systems
• Okanagan Weighted Useable Width Method• Requires field measurements• Higher risk systems
• Phase II - data collection and method test• We are within this stage of the process to date• Appling both EFN methods to selected tributaries • Documenting the process to be able to make recommendations
improvements• Timeline: due winter 2018
Methods Pilot Project
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Okanagan Tennant method
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Okanagan Tennant methodNaturalized
LT MAD
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EFN Point-of-Interest (Step1)
Okanagan Tennant Method
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Okanagan Tennant Method
Progress to date• We are at Step 4 - determining the naturalized
flow (this is in progress with AE)• Once we have these flows and can review
them then we can complete the remaining steps
An possible example of Tennant assessment
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WUW method
WUWWeighted usable width
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Reach - Nashwito 1
Habitat Type (%)Backwater Pool 0%
Beaver Pond 0%
Large Cobble/Boulder Riffle 0%
Pool Tailout 4%
Glide 17%
Primary Pool 11%
Small Cobble/Gravel Riffle 69%
Confinement - Hydro-modification (%) 65%
Riparian Function (%) 51%
WUW method
Step 2• Completed rapid
assessments of stream habitat types
• Set EFN transect
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• Determine species and life stages of interest for each creek (step 3)• For example rainbow trout
WUW method
Species Life stage # of weeks Start date End date Reference
Rainbow trout (low elevation streams)
Adult migration 12 15-Apr 10-Jul Wightman (1975)
Spawning 7 20-May 10-Jul Wightman (1975)
Incubation 8 20-May 15-Jul Ptolemy pers comm
Rearing 26 23-Apr 20-Oct Ptolemy pers comm
Juvenile migration 6 1-May 15-Jun Ptolemy pers comm
Overwintering 26 20-Oct 22-Apr Ptolemy pers comm
Also for consideration
Food Production Invertebrate DriftEcological Flows Flushing flows
IcingFreshet rampdownWetland/trib/side channel linkageChannel maintenance
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• Data collection (steps 4 – 9)• Installed 37 Glide transects and 39 riffle transects in 11 streams
• Measure water depth and velocity (habitat)• Installed 20 hydrometric stations
• Measure water level and discharge
WUW method
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• E.g. Equesis Creek• Completed habitat mapping• 4 Riffle and 4 Glide transects below
migration barrier (dam)• 3 hydrometric stations (1 real-time)
WUW method
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• E.g. Vaseux Creek • Completed habitat mapping• 2 Riffle and 2 Glide transects installed• 1 hydrometric station (real-time)
WUW method
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Progress to date
• Field work is complete
• Developing WUW curves (see next slides for Equesis Creek example)
• need AE Naturalized Flow analysis in order to complete analysis
• ONA working on developing Critical Low Flow analyses for 10 streams
• Median Naturalized Flows, Critical Low Flows, and WUW curves feed into developing Habitat Reduction Indices to be applied to water-use scenarios
• Analysis of data and comparison to Tennant method in progress (for discussions in winter 2019)
WUW method
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Draft
WUW method
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WUW method
Draft
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WUW method
Draft
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• Tennant and flow scenarios are done on a weekly scale.
• Analysis will show streams that are over-allocated, and how much of a reduction in habitat that would account for.
WUW method
Draft
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Vaseux Creek
VAS10SCR (cms)
VAS10SCR (lt MAD)
VAS30SCR (cms)
VAS30SCR (lt MAD)
Naturalized lt MAD 1.25 100 1.25 100
5% lt MAD 0.0625 5 0.0625 5
WW @ 100% ltMAD 9.69 100 10.41 100
Benthic Macroinvertebrate Production
Flow: @ 60% of Max WW 0.0200 2 0.0367 3
Non-contiguous Depth (Fish Passage)
Flow: Depth >0.24m is 25% of Max WW 1.2219 98 1.0074 81
Flow: Depth >0.18m is 25% of Max WW 0.5178 41 0.3263 26
Flow: Depth >0.12m is 25% of Max WW 0.3098 25 0.2253 18
Contiguous Depth (Fish Passage)
Flow: Depth >0.24m is 10% of Max WW 0.5135 41 0.6321 51
Flow: Depth >0.18m is 10% of Max WW 0.1949 16 0.2514 20
Flow: Depth >0.12m is 10% of Max WW 0.1392 11 0.1085 9
Kokanee Spawning WUW (from Glides)
Flow: Kokanee Spawning 0% of Max habitat 0.017 1 0.017 1
RBT Parr Rearing WUW (from Glides)
Flow: RBT Parr Rearing 0% of Max habitat 0.0205 2 0.0205 2
Critical low flows are set for:
• Fish passage
• Kokanee spawning
• Rainbow trout parrrearing
This became a new element not
established in the 2016 methods
Setting EFNs
Draft
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Reservoir Inflows
Reservoir Storage
Step 1: 1-in-2 Year Naturalized flow
Step 2: WUW Optimal EFN
Step 3: Adjusted WUW EFN
Step 4: Critical Flow Threshold
Flow required to optimize
production of juvenile rainbow
trout for example
Setting EFNs
To set the EFN values
• Customized by stream
• And by seasonal timing
• This work is in progress
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Outcomes could include: Water budget for normal year during freshet
– = Surplus
Environmental Needs
Irrigation Demand
Naturalized Flow
Setting EFNs
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Outcomes could include: Water budget for normal year during summer low
flow season
– =Deficit
Naturalized FlowEnvironmental Needs
Irrigation Demand
Setting EFNs
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Lim’limt
Prepared by:
• Kari Alex• Elinor McGrath• Joe Enns• Adam O’Dell