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Flow Alteration – Biological
Response Relationships to Assist
with the Determination of
Ecological Flows
RTI Internal Research and
Development Project
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Outline of Presentation
Objectives
Methods:
–Aquatic biota
–Flow metrics
–Statistical analyses
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Project Objectives:
To use a combined
approach of:
–unaltered and current flows
determined with WaterFALL
model
–large, state-wide aquatic biota
datasets (monitoring
programs)
to determine species-
specific flow alteration –
biological response
relationships that are
useful to water managers.
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Project Objectives:
Time for Time Approach Space for Time Approach
Time 1 –
Sp. Count = 25
Time 2 –
Sp. Count = 8
Flow alter. = 10%
Sp. Count = 25
Flow alter. = 45%
Sp. Count = 17
Flow alter. = 80%
Sp. Count = 5
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Project Objectives:
“transferable quantitative relationships between flow
alteration and ecological response” cannot be easily
developed, and “large databases, if analyzed with an eye
toward degree of flow alteration, carefully selected
response metrics, stream typology, and multiple
environmental drivers, hold the potential to reveal
important relationships” – Poff and Zimmerman (2010)
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Project Objectives:
Studies that have
adopted this
approach:
–Middle Potomac
Environmental Flows
–Virginia DEQ
Environmental Flows
–Carlisle et al. (2011) –
USGS effort across
U.S.
TNC – Middle Potomac 090811
Webinar
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Methods:
• Species
• Flow metrics
• Statistical
analyses
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Methods:
• Species
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Methods – Biological Response:
Fish:
–Top of the food chain integrators
–Relatively fast recovery time to climatic events that
may cause local extirpation
–Valued by wide segments of society
Datasets:
–NC DWQ Fish Community
–USGS National Water Quality Assessment Program
(NAQWA)
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Methods – Biological Response:
Species:
–Individual species
–Assigned to guilds indicative of flow requirements
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Methods – Biological Response:
Guilds (Persinger et al., 2010):
–based on study in North Fork Shenandoah River, VA
Guilds
Fast-generalist
Riffle
Pool-run
Pool-cover
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Methods – Biological Response:
Species:
–Individual species
–Connected to guilds indicative of flow requirements
–Species – Guild Approach:
identifies “canaries” within guilds
assign significant flow metrics to guild for management
purposes
–Up to 20 species
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Methods – Biological Response:
Species:
–Up to 20 species:
Riffle guild
Well distributed (state or regionwide)
Large number of records (i.e., > 50)
Life history stages and requirements well known
Single guild through-out life
Exploratory statistical analyses to identify species (and
associated flow metrics) with significant responses to
altered flows
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Methods:
• Flow metrics
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Methods – Flow metrics:
Selection criteria:
–Biologically relevant
–Amenable to management
–Can be expressed as % change
–Can be effectively modeled with WaterFALL
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Methods – Flow metrics:
Biologically relevant:
–Review of flow-biology hypotheses for fish:
Increases and decreases in low, high and median/stable/base
flows
Important events all months of the year
–Represent the five components of flow
Magnitude, timing, duration, frequency, rate of change
Amenable to Management:
–Magnitude, timing, duration, frequency, rate of change
–Focus on low flows and reductions in flow
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Methods – Flow metrics:
Selection criteria:
–Biologically relevant
–Amenable to management
–Expressed as % changes
–Can be effectively modeled
Flow metrics
–TNC Indicators of Hydrologic Alteration (IHA) = 67 metrics
–Additional metrics
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Methods – Flow metrics
Monthly Measures Annual Measures
Extreme low flow (10th
percentile)
3-, 7-, 30-, and 90-day minimum
Low flow (25th percentile)3-, 7-, 30-, and 90-day maximum
Median/Base flow (50th
percentile)
Extreme low flow (10th
percentile)
High flow (75th percentile)Extreme low flow count
Extreme low flow duration (longest
duration during year)
bold = IHA metrics
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Methods – Flow metrics:
Flow metric calculations:
–WaterFALL hydrographs for unaltered/historic and
current condition:
Unaltered/Historic = Potential Natural Vegetation (PNV) or
1970s land-cover
Current = 2006 NLCD + sources of instream flow alteration
(dams, withdrawals, discharges)
–30+ years of climate data
–Expressed as % change
–Focus analyses on reductions in flow
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Methods:
•Statistical
analyses
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Methods – Statistical analyses:
Multiple and Single Predictor Analyses:
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Methods – Statistical analyses:
Multiple Predictor Analysis Single Predictor Analysis
Predictor 1
Re
s
p
o
n
s
e
Y = a + b1*X1 + b2*X2 +..+ bp*Xp
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Methods – Statistical analyses:
Multiple and Single Predictor Analyses:
–Multiple Predictors:
Multiple regressions (or comparable non-parametric
analyses)
Benefits:
gain a better understanding of the degree to which
species is influenced by altered flows versus other
factors
reduces the amount of error (i.e., accounts for a
larger proportion of the variance in the relationship)
Y = a + b1*X1 + b2*X2 +..+ bp*Xp
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Methods – Statistical analyses:
Multiple and Single Predictor Analyses:
–Multiple Predictors:
Negatives:
Application of relationship is restricted to locations
where have data for the other factors (or need to
assume default or average values for factors)
Complicates the flow alteration – biological response
relationship
Co-variates included in analysis = measures of water
quality, channel morphology, habitat, climatic events,
sampling date, interspecific interactions
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Methods – Statistical Analyses
Component Attribute/Dataset
Water Quality DO, pH, conductance (DWQ Habitat and
USGS NAQWA datasets)
303d listing
Channel Morphology Sinuosity/Linear Length
Slope
Physiographic Region
Habitat NC Habitat Score (DWQ Habitat dataset)
Fragmentation x 2 (stream length between
obstructions) – same stream length and
summed stream length of network
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Methods – Statistical Analyses
Component Attribute/Dataset
Climatic Events Preceding year total precipitation
Average of preceding 3 years of total
precipitation
Date Sampling Month
Interspecific
Interactions
Influence of exotic and injurious introduced/
exotic fish species
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Methods – Statistical analyses:
Multiple and Single Predictor Analyses:
–Single Predictor:
linear or quantile regressions (or comparable non-
parametric analyses)
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Methods – Statistical analyses:
Linear Regression
Predictor 1
Re
s
p
o
n
s
e
Quantile Regression
TNC – Middle Potomac
090811 Webinar
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Methods – Statistical analyses:
Multiple or Single Predictor Analyses:
–Singe Predictor:
linear or quantile regressions (or comparable non-
parametric analyses)
Benefits:
Only based on response to % change of flow
metric, so application in water management is more
straight forward
Negatives:
Potentially large amount of error which will reduce
the strength of the relationships
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Methods – Statistical analyses:
Multiple or Single Predictor Analyses:
–Combination of analyses provides:
water managers with an understanding of the relative
importance of flow alterations and other influential variables
for each species
Flow-biology relationships with which to model/predict the
impacts of flow alteration on biological responses
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Questions:
Fall Creek