Estimating Daily Streamlow at Ungaged Sites in NH: Negative - - PowerPoint PPT Presentation

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Estimating Daily Streamlow at Ungaged Sites in NH: Negative - - PowerPoint PPT Presentation

Estimating Daily Streamlow at Ungaged Sites in NH: Negative Run-length Assessment Neil M. Fennessey HYSR/Hydrologic Services HYSRConsult@gmail.com NH Department of Environmental Services Concord, NH August 27, 2018 Estimating Daily Flows at


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Estimating Daily Streamlow at Ungaged Sites in NH: Negative Run-length Assessment

Neil M. Fennessey HYSR/Hydrologic Services

HYSRConsult@gmail.com

NH Department of Environmental Services Concord, NH August 27, 2018

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Estimating Daily Flows at Ungaged Sites

 NH DES needs to determine PIFs at ungaged sites

in presently and future designated rivers

 NHDES needs a reliable way to estimate daily

streamflow time series at these ungaged sites

 The QPPQ Transform method is one approach  Conceived and developed by Fennessey (1994)  Has been used in the northeast and central US,

Canada and South Africa

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Other Ways to Estimate Daily Flows at Ungaged Sites: Pluses & Minuses

 Watershed Area Ratio (WAR) method  Very simple to use  Assumes that all watersheds are exactly alike

except for the size of the watershed

 Rainfall-Runoff Models (HSPF, Sacramento Soil

Moisture Accounting Model)

 Physically based but parameter-intensive  Used by NOAA for flood forecasting  Requires long stream gage period-of-record for

site calibration and validation

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 The QPPQ Transform method has been adopted

  • r is being considered by several US Geological

Survey district offices:

 Massachusetts and Rhode Island USGS  Pennsylvania USGS  Iowa USGS  Minnesota USGS  New York USGS  New Hampshire and Vermont USGS

Does USGS Like QPPQ Transform?

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 The QPPQ Transform method was extensively

tested by the USGS and bested 17 alternative methods for estimating daily flow time series at 182 gaged watershed sites located in

 West Virginia  Tennessee  North Carolina  South Carolina  Georgia  Alabama  Florida

Has the QPPQ Been Extensively Tested?

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 The QPPQ Transform method has been adopted

by several state agencies:

 Massachusetts EOEEA  Massachusetts DEP Water Management Act

program

 Sustainable Water Management Initiative  The Delaware River Basin Authority  Maryland Dept. of the Environment  Pennsylvania Dept. of Environmental Protection  New York State Energy R & D Authority  Minnesota Pollution Control Agency

Have States or Agencies Adopted the QPPQ?

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 The QPPQ Transform method has been used for  Many surface water reservoir system

assessments in Massachusetts and Connecticut

 River basin and watershed studies in

Massachusetts and Connecticut

 Systems analysis study of the Connecticut

River watershed

 Complex litigation in Connecticut

Examples of Local Applications

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The QPPQ Transform Method

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Four Steps to the QPPQ Transform Method

  • 1. Chose a USGS Streamgage Site for the time

series: Qgage(t)

  • 2. Use that time series to construct a streamflow

duration curve (FDC): Qgage(p)

  • 3. Construct a FDC at the ungaged site using its

watershed’s soil characteristics, climate, and topography and a regional FDC model: Qungaged(p)

  • 4. Generate a streamflow time series at the

ungaged site: Qungaged(t)

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Minnesota

USGS

(Lorenz and Zigeweid, 2016)

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Use Qgage(t) to Construct ‘observed’ FDC Qgage (p)

 Rank sort Qgage(t) “n” days from largest to smallest

Q(1) ≥ Q(2) ≥ Q(3) … Q(n-2) ≥ Q(n-1) ≥ Q(n)

POR 30 years x 365 = 10,950 days P[Q≥Q(n)]x100 =10,950/10951 x 100 = 99.991

 “i” is the rank-order i=1,n  “n” is number of days in the period of record  Use “plotting position” formula to estimate

exceedance probability p=P[Q≥q]

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Step 1: Qgage(t) and Step 2: Qgage(p)

 Common factor between the flow date, time, and

the FDC probability, p, is Q = a 3-D relationship

 Knowing Q gage (t) & p(Qgage) => p(t)

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Step 3: Regional FDC Model

 Construct a FDC for the ungaged site without

historic daily streamflow data

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HYSR Phase 1 Study for NH DES: Update Regional FDC Model

 Fennessey (2018) developed a special

streamgage network of 133 USGS gaged watersheds in New England, NY, PA and NJ.

 Daily streamflow data: minimum 20-year POR in

1950-1990 base period.

 Research confirmed earlier Fennessey (1994)

finding that the 3-parameter Generalize Pareto (GPA) was the best among alternatives.

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 L-moments used to estimate the 3 GPA

parameters: ζ, α, κ for each of 133 HYSR sites

 Gather watershed specific data for each of these

133 USGS gage sites in the HYSR network

 Use each of the 3 GPA parameters statistically

determined for each HYSR watershed from obs streamgage data as dependent variables

 Use OLS multivariate regression and each

watershed’s specific soil, climate, and topography data as candidate independent variables

 Keep only “statistically significant” soil, climate,

and topographic variables to create one equation for each GPA parameter; ζ, α and κ .

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 To construct a FDC at the ungaged site, the analyst

must determine ten soil, climate, and topography characteristics for that watershed:

 Watershed area (mi2)  Avg annual precipitation (in/yr)  Avg annual temperature (oF)  Potential maximum soil moisture retention (in)  Percent of watershed area covered by HSG C soil (%)  Avg watershed elevation (ft)  Avg watershed aspect (degrees) 0-360O  Percent of watershed area covered by lakes, ponds and

reservoirs (%)

 Percent of watershed area covered by impervious surface (%)  Slope of main stream channel (ft/mile)

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Compare FDCs and Assess “Goodness-of-Fit” HYSR Phase 1 (Fennessey, 2018)

 Construct “observed,” “fitted,” and regional “model”

FDCs at eleven NH USGS gages sites, watershed areas range: 12.1 mi2 – 622 mi2

 Graph all three FDCs for visual comparison  Estimate the Bias between the “observed” FDC and

the “fitted” FDC to see how suitable the GPA is as basis for the Reginal FDC Model

 Estimate the Bias between the “observed” FDC and

the regional “model” FDC to see how well it compared with the “fitted” FDC.

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Baker River, near Rumney, NH

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QPPQ Transform Steps 1 - 3

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 Assume for Steps 2 and 3: p(Qungaged) = p(Qgaged)

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Step 4: Generate Qungaged(t)

 Recall 3-D relationship between t, Q and p => p(t)  Use regional FDC model with p(t) instead of just p

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HYSR Phase 2 Study for NHDES Negative Run-length QPPQ Transform Assessment

 In the Phase 2 study, HYSR focused on a negative

run-length analysis of daily flows during bioperiods determined by fishery and other specialists at five USGS streamgage sites in New Hampshire

 HYSR and NHDES reasoned that since Protected

Instream Flow rates, PIFs, are determined in part by sub-threshold event durations, a negative run- length analysis would be a good way to further assess the QPPQ Transform method for use in New Hampshire

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A Negative Run-length

 A negative run-length event occurs when

streamflow, Q(t), falls below a designated threshold, QP, for one or more consecutive days.

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Bioperiods

 The University of New Hampshire et al (2007) study

determined six PIF bioperiods for the Souhegan R.

No. Bioperiod Start End 1 Over-Wintering 15-Nov 28-Feb 2 Spring Flood 1-Mar 30-Apr 3 Shad Spawning 1-May 14-Jun 4 GRAF Spawning 15-Jun 14-Jul 5 Rearing & Growth 15-Jul 30-Sep 6 Salmon Spawning 1-Oct 14-Nov

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 The participants of the New Hampshire et al (2007)

Souhegan River watershed study developed PIFs for each bioperiod

 HYSR used two of these PIFs for the present study

as negative run-length thresholds: Qcritical and Qrare.

 HYSR used Q85 and Q95 for the Diamond, Saco,

Oyster and Pemigewasset Rivers because these watersheds do not yet have PIF flow rates.

 Of particular interest to NHDES is the Rearing &

Growth bioperiod which begins mid-summer and ends in early fall, when yearly flows are usually the lowest and the aquatic ecosystem quite stressed.

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 During the 1963-1968 Rearing & Growth bioperiod,

flows fell below Qcritical (yellow) and Qrare (red) for long runs of time.

Q (cfs)

1 10 100 1 10 100

Year

1964 1966 1968

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 During all Rearing & Growth days of flow over the

entire POR, the FDC shows what fraction of time. Qcritical ≈ Q75,rearing & growth and Qrare ≈ Q90,rearing & growth

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 By counting the number of nday-long negative run-

length events one constructs a frequency histogram for sub-Qcritical events during Rearing & Growth.

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 Similarly, one constructs a frequency histogram for

sub-Qrare events that occurred over the POR during the 77 day-long Rearing & Growth bioperiod.

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 If one wants to estimate the likelihood that a

negative run-length of nday or more given that flows are sub-Qcritical, one constructs a probability plot.

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 Similarly, one may construct a probability plot for the

negative run-length of nday or more given that flows are sub-Qrare. Called a Run Duration Curve (RDC)

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Further QPPQ Transform Assessment

 The QPPQ Transform is assessed by comparing

negative run-length, season-specific FDCs, frequency histograms and probability plot RDCs.

 Souhegan River assessment used Qcritical and Qrare

as event thresholds

 Diamond, Saco, Oyster and Pemigewasset River

assessments used Q85 and Q95 as event thresholds

 Tests at these five sites were run using two different

Index gages from the Fennessey (2018) 133 gage network as needed for Step 1 and 2 of the QPPQ Transform: HCDN NN and HCDN NN WA.

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 The Obs. and QPPQ Transform HCDN NN Rearing

& Growth bioperiod FDC

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 The Obs. and QPPQ Transform HCDN NN WA

Rearing & Growth bioperiod FDC

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod negative run-length histograms for Qcritical threshold HCDN NN HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod negative run-length histograms for Qrare threshold HCDN NN HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod negative run-length RDCs for Qcritical threshold HCDN NN HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod negative run-length RDCs for Qrare threshold HCDN NN HCDN NN WA

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Still More QPPQ Transform Assessments

 The QPPQ Transform is further assessed by

comparing:

 the bioperiod specific total number of negative

run-length events over the entire POR

 the 95% confidence interval of the mean duration,

E[durat] of a negative run-length event

 the coefficient of determination, R2 between the

POR and season-specific obs. daily data and specific QPPQ transform Index gage daily flow pair for both HCDN NN and HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod number

  • f negative run-length events for both Qcritical and

Qrare over the POR HCDN NN HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA Rearing & Growth bioperiod 95% CI

  • f the mean duration of negative run-length events,

E[durat] for both Qcritical and Qrare over the POR

Obs Qcrit QPPQ Qcrit Obs Qrare QPPQ Qrare

Event Duration (days)

5 10 15 20 Obs Qcrit QPPQ Qcrit Obs Qrare QPPQ Qrare

Event Duration (days)

5 10 15 20

HCDN NN HCDN NN WA

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 The Obs. and QPPQ Transform HCDN NN and

HCDN NN WA POR and bioperiod R2 . Souhegan watershed area = 170.2 mi2

Obs and QPPQ NN Obs and QPPQ NN WA NN & NN WA Watershed areas: 129.5 mi2 147.4 mi2 Centroid-to-Centroid Distances: 24.6 miles 33.2 miles R2 (%) R2 (%) POR 34.2 68.5 Bioperiod Over-Wintering 30.7 74.5 Spring Flood 13.4 61.2 Shad Spawning 34.6 79.5 GRAF Spawning 57.0 63.4 Rearing & Growth 26.8 57.1 Salmon Spawning 27.1 57.1

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The Final Tally

 HYSR examined the R2 tables and 178 graphs

found in the appendices of the Phase 2 study report.

 HYSR determined that by a 2 to 1 margin, the

HCDN NN was the better choice than the HCDN NN WA when using the QPPQ Transform to estimate daily flows at ungaged sites in New Hampshire

 With both phases of the HYSR study complete,

NHDES will be able to make an informed decision about adopting the QPPQ Transform method as the preferred way to estimate a long period time series

  • f daily flows at ungaged sites in New Hampshire.
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Summary

 The QPPQ Transform method was conceived and

developed by Fennessey (1994)

 The method has been widely adopted  The Step 3 regional FDC model was updated and

the QPPQ Transform broadly assessed for accuracy

 The goals of the QPPQ Transform remain the same:  Provide a method to generate a quality time

series of daily streamflow data at ungaged sites

 Allow the analyst the freedom to choose to do

whatever they want with the generated time series, Qungaged(t) as they would Qgage(t)

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Questions and Comments?

Neil M. Fennessey Hydrologic Services 49 School Street South Dartmouth, MA 02748 HYSRConsult@gmail.com