HomeMy WebLinkAboutStakeholderMeeting_2_12052023September 25, 2023
Neuse River
Watershed Modeling
stakeholder Meeting
RESPEC.COM
Agenda
›Project Introduction – DWR
›Review of Model Selection and Model Period Determination
›Quality Assurance Project Plan (QAPP)
›Simulation and Data Source Planning
›Updates on Model Development
›Updates on Model Calibration and Validation
›Remaining Timeline
›Discussion
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RESPEC TEAM
›Principal-In-Charge – RUSSEL Persyn
›Project Manager – Seth Kenner
›QA/QC Officer – Paul Duda
›Modeling Team
⁄Chris Lupo
⁄Cindie Kirby
⁄Paul Hummel
3
Project Overview
›Schedule
4
Model Selection
›Hydrologic Simulation Program-Fortran
⁄Vetted for over 40 Years
⁄Core watershed model in US-EPA BASINS and US ACE Watershed Modeling System
⁄Capable of continuous hourly simulation
⁄Represents multi-land use watersheds
⁄Works for multiple pollutants (sediment, nutrients, dissolved oxygen, etc.)
⁄Represents surface, subsurface, stream, and lake hydrology and water-quality processes,including point sources
⁄RESPEC modeling team
•Over 50 years of experience
•Hundreds of model applications
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HSPF Model
Calibrated
Parameters
⁄Hydrology
⁄Sediment
⁄Temperature
⁄Dissolved oxygen
⁄Phosphorus Species
⁄Nitrogen Species
Model Development
6
Cropland Barren UrbanForestPastures
Overland Flow
Interflow
•Precipitation
•Air Temperature
•Evaporation
•Solar Radiation
•Cloud Cover
•Wind
•Dew Point
Model Land Covers and Soils
Point Sources
In-Stream Processes
-Nutrient Cycling
-Fate and Transport
Model Parameterization:
Infiltration
Cover
Shade
Upper/lower zone storage
Groundwater recession
Ice parameters
Interception storage
Interflow
Manning’s n
Vegetation
CLimate
BMP Module Implementation Planning
Modeling Period
›2004-2022
⁄Wet and dry years
⁄2003 as “warm up period”
7
0
20
40
60
80
100
120
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019 2020 2021 2022
Precip (inches)
Station: Richlands (316422)Station: Jacksonville Eoc (314471)Station: Albert Ellis Airport (KOAJ)Station: Sandy Run (CLJN7)
Quality Assurance Project Plan
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data Collection
›Meteorological Data
⁄PRISM
⁄NLDAS
›Atmospheric Deposition
⁄NADP
⁄CASTNET
›Discharge
⁄USGS NWIS
›Water Quality
⁄USGS NWIS (from WQ portal)
⁄State WQ Data
›Point Source
⁄State Data
›Water Use
⁄State Data
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›Land Cover
⁄NLCD 2019
›Soils
⁄SSURGO
›Cropland
⁄NASS Crop Data Layer
›Feedlots
⁄State Layer
›MS4s
⁄State Layer
›Septic
⁄State Sewered Areas
⁄Census Spatial Data
›Watersheds
⁄NHD Plus V2
›Flowlines
⁄NHD PLUS HIGH RES
⁄Local Data
›Elevation/slope
⁄USGS 3Dep
›Cross Sections
⁄NC Flood Risk Information System HEC Models
Gridded Met Data
›A script estimates meteorological inputs for HSPF with gridded data for each meteorological zone
›The inputs are exported to a WDM file that HSPF reads.
›The list of timeseries inputs includes:
⁄Parameter-elevation Regressions on Independent Slopes Model (PRISM)
•4-KM grid
•Daily time-step
•Precipitation
⁄North American Land Data Assimilation System (NLDAS)
•12-km grid
•Hourly time-step
• Precipitation – used to disaggregate PRISM
•Air temperature
•Solar radiation
•Wind speed
•Calculated from NLDAS timeseries
•Dew point – specific humidity, relative humidity, and atmospheric pressure (two method options)
•Cloud cover – solar radiation
•Potential evapotranspiration – solar radiation, dew point, air temperature, and wind travel
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MET ZONE Development
›Met Zone Definition
⁄Subwatersheds sharing the same precipitation time-series
⁄Land uses in these zones share the same parameter sets
›Steps
⁄Obtain precipitation for each subwatershed
⁄Produce correlation and adjacency matrices
⁄Use analysis to aid the Aggregation of subwatersheds
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MET ZONE Development
Correlation Matrix
12
Adjacency Matrix
›Additional considerations
⁄Drainage Areas
⁄Average Annual Precipitation
⁄Abrupt Changes in Soils, Landuse, Topography, or Ecoregion
Fill/Process Other Timeseries Data
›Atmospheric Deposition (N Species)
⁄Convert Weekly or monthly to a daily Timestep
⁄Fill with interpolation and monthly averages
›Water Use
⁄Surface and Groundwater Timeseries filled with Monthly Averages by Reach
›Continuous Discharge for Calibration
›water quality for calibration (Some continuous, mostly grab)
›Point Sources – Data supplied by NC DWR
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Point Source QA/QC
›Plots and Stats Generated
⁄Min, Mean, Max, Etc.
⁄Review Complete
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Point Source QA/QC
›Review Edits Sent to NC DWQ (Plots and Changes)
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Point Source QA/QC
›Timeseries And External Source Blocks Generated for Model
⁄Generated using Point Source tool so easily updated if more changes occur
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Point Sources
›Fill Missing Data For Continuous Daily Timeseries
⁄Fill missing constituents using default concentrations
▪Uses ratios if at least 1 component is available
▪Uses concentrations directly if no components are available
⁄Interpolate if missing gap < 14 days
⁄Fill with monthly averages
⁄Fill with overall average
⁄Fill with default concentrations
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Point Sources
›Missing Data – Default Concentrations (mg/L)
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Description Class Type NOX TAM ORN TN BOD PO4 ORP TSS
Industrial Process & Commercial Wastewater
Discharge Ind Continuous 7 2 1 10 1.44 0.1 0.02 1
Discharging 100% Domestic < 1MGD Class D Continuous 3 1 2 6 1.44 1.6 1.1 1
Municipal Wastewater Discharge, Large Class A Continuous 15 3 1 19 1.44 2.76 0.02 1
Water Plants and Water Conditioning Discharge WTP Intermittent 3 1 0 4 1.44 0.1 0.02 1
Municipal Wastewater Discharge, < 1MGD Class C Continuous 7 1 2 12 1.44 2.59 0.99 1
Water Plants and Water Conditioning Discharge WTP Continuous 3 1 0 4 1.44 0.1 0.02 1
Industrial Process & Commercial Wastewater
Discharge Ind Intermittent 7 2 1 10 1.44 0.1 0.02 1
Covation Biomaterials Kinston Site NC0003760_1 Ind_C Continuous 7 2 1 10 3.12 0.1 0.02 5.8
Lee Steam Electric Plant NC0003417_1 Ind_L Intermittent 1 2 1 4 2.1 0.1 0.02 1
New Bern Cellulose Fibers NC0003191_1 Ind_N Continuous 7 2 1 10 1.44 0.1 0.02 9
Greenville Lumber Facility NC0073229_1 Ind_G Intermittent 7 2 1 10 1.44 0.1 0.02 0.1
Ward Transformer Company NC0045608_1 Ind_W Intermittent 1 2 1 4 1.44 0.1 0.02 0
Point Sources
›Default Speciation (When Not Enough Existing Data)
⁄TSS - 60% Clay, 40% Silt
⁄NOX – 98% NO3, 2% NO2
⁄TP – 72% PO4, 28% Organic P
⁄BOD – to BOD Ultimate (Factor = 2.4)
⁄BOD to Organic N – 4% of BOD
⁄BOD to Organic C – 12% of BOD Concentration
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Subwatershed Delineation
›Boundary Condition at Falls Lake Outlet
›Breaks at:
⁄Most HUC12 outlets
⁄Applicable parameter impairment outlets
⁄Significant flow and water quality monitoring sites
⁄Modeled lakes
›National Hydrography Database v2
⁄Hydrologically corrected digital elevation model
•Flow accumulation grid
•Flow direction grid
⁄Errors occur using NHD high-resolution database
⁄ArcGIS pro hydrology toolset
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Modeled Reservoir/Lake Selection
›7 Lakes/Reservoirs
⁄Impaired (1)
⁄Connected and >200 acres
⁄Calculate surface area at volumes and depths of contours if bathymetry is
available
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Lake/Reservoirs Size (Acres)Impaired
Lake Johnson 148 Yes
Holts Lake 379 No
Lake Crabtree 455 No
Lake Benson 476 No
Wiggins Mill Reservoir 511 No
Lake Wheeler 565 No
Buckhorn Reservoir 758 No
Reach Development
›National Hydrologic Dataset High-Resolution Flowlines
›Reduced to One Reach per Subwatershed
›Calculations for HSPF:
⁄Length
⁄Slope
⁄Elevation
⁄F-tables
•At a range of depths
•Surface area
•Volume
•Flow
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Reach/Lake FTABLE Development
›Function table (FTABLE)
⁄Summary of hydraulic properties (extended rating curve)
⁄For each depth/stage
•Surface area
•Volume
•Outflow
›Lake Data
⁄Outflow information (dams)
›Reach Data
⁄Cross sections
•Hydraulic models (have a LOT!!!)
•Surveys
•DEM/Lidar
•Streamflow field measurements/gaging notes
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Schematic Development
›Model Land Cover In each Subwatershed
⁄Evaluate
•National Land Cover Dataset 2019
•NRCS gNATSGO Soils hydrologic soil group
•Crop types
•Tile drainage
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Developed
16%
Forest
28%
Scrub/Shrub
2%Herbaceous
2%
Hay/Pasture
4%
Cultivated
Crops
24%
Wetland
24%
A
19%
B
19%
C
9%
AD/BD/CD/D
53%
Soybeans
45%
Corn
24%
Dbl Crop
WinWht/Soybean
s
8%
Fallow/Idle
Cropland
6%
Cotton
6%
Sweet Potatoes
4%
Tobacco
3%
Other
4%
Schematic Development
›Tile Drainage Estimation
⁄Row crops
⁄Less than 4% slope
⁄Hydrologic Soil Group A/D, B/D, C/D, D
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D. Wall, Gosack, B., Pearson, T., Shore, M., 2017. Estimating Tile Drainage Densities. Prepared by Minnesota Pollution Control Agency and Minnesota Department of Environmental Resources
Schematic Development
›Manured Cropland
⁄Evaluate estimation by subwatershed
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Method used in Chesapeake Bay Watershed Mode:
https://cast-content.chesapeakebay.net/documents/5%20Land%20Use%202020%2003%20Draft.pdf
Schematic Development
›MS4s
⁄Used Provided MS4 layers
⁄Have separate mass links for easy tracking
›Septic Systems
⁄Used Census Population points outside of Areas with Sewer Systems
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Land Use Aggregation
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Final Segmentation
›Putting it all together
⁄Produce the schematic
•Links all source areas to a reach
›Initial Model parameterization
⁄Past modeling efforts
•Pawcatuck
•CTWM (2001)
•Octoraro
⁄GIS Data
•Slope
•Elevation
•Soil properties
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Land Cover
Impervious
MS4
Hydrozones
HSG
Sewered/Blockpop
Calibration vs validation
›Calibration
⁄Adjust model parameters through an iterative trial and error-process until the
resulting predictions provide a good correlation with observed data
›Validation
⁄Test of the calibration on a separate time-period to help establish greater
confidence in the calibration and predictive capabilities
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Calibration Criteria
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›How good is good enough?
hydrology - Calibration Sites
›Boundary Condition (1)
⁄Falls Lake
›Primary Sites (5)
⁄Mainstem or large drainage area with full POR (Contentnea Creek)
›Secondary Sites (8)
⁄Relatively smaller drainage area with nearly or full POR
›Tertiary Sites (15)
⁄Smallest drainage areas with short POR
⁄Often upstream of a more robust gage
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Hydrology Calibration
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›Phases for hydrology calibration
⁄Establish an annual water balance
⁄Adjust low-flow/high-flow distribution
⁄Adjust storm flow/hydrograph shape
⁄Make seasonal adjustments
R2 mfe R2 mfe Vol [in]Peak [cfs]
130 USGS-02087500 Neuse River 406.3 100 Primary 0.99 0.98 0.94 0.93 9.0 4.5 5.5 Very Good
350 USGS-02089000 Neuse River 1686.7 100 Primary 0.96 0.95 0.87 0.84 2.9 9.6 -0.3 Good
470 USGS-02089500 Neuse River 2042.4 100 Primary 0.95 0.94 0.92 0.89 3.3 6.1 -2.1 Fair
595 USGS-02091500 Contentnea Creek 733.8 100 Primary 0.89 0.88 0.79 0.74 3.6 9.5 -0.5 Poor
630 USGS-02091814 Neuse River 3257.6 99 Primary 0.92 0.91 0.87 0.85 3.2 -1.6 -0.4
41 USGS-02087324 Crabtree Creek 121.9 100 Secondary 0.94 0.92 0.84 0.80 4.8 2.8 9.2
81 USGS-02087359 Walnut Creek 29.8 100 Secondary 0.92 0.81 0.79 0.79 11.2 -13.7 14.6
175 USGS-02088000 Middle Creek 83.6 100 Secondary 0.92 0.88 0.65 0.63 12.2 -13.4 12.5
189 USGS-0208773375 Swift Creek 120.1 75 Secondary 0.91 0.78 0.75 0.73 14.0 -22.1 15.6
331 USGS-02088500 Litte River 229.7 100 Secondary 0.92 0.92 0.80 0.80 0.0 -10.6 3.2
544 USGS-02090380 Contentnea Creek 157.3 100 Secondary 0.86 0.85 0.77 0.77 -1.0 -20.8 5.7
589 USGS-02091000 Nahunta Swamp 79.8 100 Secondary 0.86 0.84 0.75 0.74 9.6 -12.8 -0.4
731 USGS-02092500 Trent River 174.5 100 Secondary 0.90 0.89 0.65 0.61 -6.7 0.9 -4.8
33 USGS-0208726005 Crabtree Creek 60.7 100 Tertiary 0.93 0.92 0.80 0.78 -2.6 -0.5 8.7
35 USGS-02087275 Crabtree Creek 108.9 100 Tertiary 0.94 0.88 0.80 0.73 8.2 8.0 17.0
47 USGS-0208732885 Marsh Creek 9.6 100 Tertiary 0.83 0.75 0.83 0.83 5.1 -18.8 11.2
71 USGS-02087337 Walnut Creek 3.3 23 Tertiary 0.60 0.58 0.68 0.61 -9.5 -45.5 -1.0
73 USGS-0208734210 Walnut Creek 9.1 23 Tertiary 0.83 0.69 0.68 0.68 4.3 -23.5 10.4
75 USGS-0208734795 Walnut Creek 17.2 23 Tertiary 0.89 0.81 0.80 0.79 5.0 -23.1 7.8
77 USGS-0208735012 Rocky Branch 1.2 100 Tertiary 0.81 0.75 0.83 0.81 0.5 -23.0 9.1
91 USGS-0208739674 Neuse River Trib 2.3 6 Tertiary 0.44 0.31 0.31 0.18 -37.0 -79.5 -34.9
181 USGS-02087580 Swift Creek 24.9 100 Tertiary 0.82 0.47 0.64 0.61 21.5 -23.6 36.7
182 USGS-0208758850 Swift Creek 35.8 100 Tertiary 0.84 0.58 0.66 0.63 21.8 -28.5 29.2
317 USGS-02088383 Litte River 53.4 75 Tertiary 0.87 0.86 0.67 0.66 -2.8 -37.1 -2.4
435 USGS-0208925200 Bear Creek 57.5 63 Tertiary 0.84 0.76 0.79 0.61 3.4 1.1 -11.5
553 USGS-02090504 Contentnea Creek 242.4 10 Tertiary 0.69 0.61 0.50 0.43 3.9 -29.5 4.8
605 USGS-02091736 Middle Swamp 49.4 6 Tertiary 0.47 -0.38 0.68 0.03 29.1 4.9 51.6
687 USGS-0209205053 Swift Creek 251.8 24 Tertiary 0.88 0.80 0.79 0.76 -12.4 -26.9 -19.9
Calibration
TypeReachGageSegment Name
Drainage
Area [sq mi]
Percent
Available Criteria
Monthly Daily Storm Differences Total Vol
%Diff
hydrology Calibration Statistics
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hydrology Calibration Statistics
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R2 mfe R2 mfe Vol [in]Peak [cfs]
Area Weighted 0.92 0.90 0.85 0.82 3.3 0.4 0.3 Very Good
True Average 0.84 0.75 0.74 0.69 3.7 -14.5 6.2 Good
Area Weighted 0.83 0.78 0.78 0.68 11.5 12.0 9.9 Fair
True Average 0.87 0.77 0.76 0.66 11.5 -2.4 16.2 Poor
Area Weighted 0.89 0.88 0.83 0.81 1.5 0.8 -1.2
True Average 0.89 0.80 0.79 0.76 4.2 -11.1 6.2
Averaging
Method
Full Calibration
(2004-2022)
Dry Validation
(2004-2011)
Wet Validation
(2012-2016)
Period Criteria
Monthly Daily Storm Differences Total Vol
%Diff
R2 mfe R2 mfe Vol [in]Peak [cfs]
Area Weighted 0.92 0.90 0.85 0.82 3.3 0.4 0.3 Very Good
True Average0.84 0.75 0.74 0.69 3.7 -14.5 6.2 Good
Area Weighted 0.83 0.78 0.78 0.68 11.5 12.0 9.9 Fair
True Average0.87 0.77 0.76 0.66 11.5 -2.4 16.2 Poor
Area Weighted 0.89 0.88 0.83 0.81 1.5 0.8 -1.2
True Average0.89 0.80 0.79 0.76 4.2 -11.1 6.2
Averaging
Method
Full Calibration
(2004-2022)
Dry Validation
(2004-2011)
Wet Validation
(2012-2016)
Period Criteria
Monthly Daily Storm Differences Total Vol
%Diff
SNOWDAS SNOWFALL
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Area % Dif
Upper 10.8
Middle 15.6
Lower -20.7
Overall 5.3
Area % Dif
Upper 6.0
Middle 0.2
Lower -34.3
Overall -5.3
SNOWDAS Snow Depth
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Area % Dif
Upper 6.0
Middle 0.2
Lower -34.3
Overall -5.3
SNOWDAS Snow Depth
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Mainstem Timing and Peak Flow Challenges
›Mainstem Neuse River and Contentnea Creek
⁄Over-simulating peak flow, poor daily statistical performance, and peak timing was being simulated up to 5 days early
⁄Issue Resolutions:
•Recalculated stream slopes using the 5th and 95th percentile elevations instead of min and max (better agreement with HEC-RAS profiles)
•Provided additional storage volume as a function of stream top width and depth (justified with ecoregion descriptions)
›Tributary and Smaller Headwater Streams
⁄Under-simulating peak flow
⁄Issue Resolutions:
•Capped HEC-RAS obtained Manning’s n for floodplain (values were >1 for ~1/8th of the tributaries)
•Improved runoff calibration with infiltration and surface storage parameters
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Mainstem Timing and Peak Flow Challenges
›EPA Level IV Ecoregions
⁄Downstream portions of the Neuse and Contentnea are categorized as “Southeastern Floodplains and Low Terraces”
⁄“…the region includes large sluggish rivers and backwaters with ponds, swamps, and oxbow lakes.”
hydrology - Mainstem Timing Challenges
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hydrology - Mainstem Timing Challenges
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Water Balance Results
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0 20 40 60 80
Surface Runoff
Groundwater
Runoff
Evaporation
Deep Loss
Water Balance Comparison
Neuse HSPF Cape Fear SWAT NCDEQ Piedmont NCDEQ Coastal Plain
›Comparable to two independent studies in the region
⁄Cape Fear SWAT Model
⁄2009 Cape Fear Basin Plan
›Ensures HSPF runoff parameters are well calibrated and provides further justification for needing to adjust storage volume in FTABLES
›Water balances also make sense on a relative landuse basis
⁄ex: runoff for develop >> forest
Water Quality Calibration Sites
›Primary (3)
⁄>10,000 samples
⁄Downstream on major drainages
›Secondary (24)
⁄> 1,000 samples
⁄Substantial drainage area, key locations, modeled lakes
›Tertiary (40)
⁄>1,000 samples
⁄Upstream of areas already covered by secondary locations
⁄Only reviewed when inconsistencies are observed at downstream secondary locations
›NA
⁄< 1,000 samples or on an estuary
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Water Quality Calibration process
›Phases for Water Quality calibration
⁄Estimate land-use-specific parameters
⁄Compare simulated loading rates with expected ranges and adjust if necessary
⁄Calibrate instream parameters to observed data
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Land-use
Frink's Export Coefficients
(lb/ac/yr)
CTWM Export Coefficients
(lb/ac/yr)
Total Nitrogen Total Phosphorus Total Nitrogen Total Phosphorus
General Urban 12.0 ± 2.3 1.5 ± 0.2 NA NA
Pervious Urban NA NA 8.5 (5.6–15.7)0.26 (0.20–0.41)
Impervious Urban NA NA 4.9 (3.7–6.6)0.32 (0.18–0.36)
Agriculture 6.8 ± 2.0 0.5 ± 0.13 5.9 (3.4–11.6)0.30 (0.23–0.44)
Forest 2.1 ± 0.4 0.1 ± 0.03 2.4 (1.4–4.3)0.04 (0.03–0.08)
Wetland NA NA 2.2 (1.4–3.5)0.03 (0.02–0.05)
0
2
4
6
8
10
12
14
16
TN Loading Rate [lb/acre/yr]TN Loading Rates - Example
Calibration Process Overview
›Water Quality Calibration
⁄Sediment
⁄Dissolved oxygen
⁄Temperature
⁄Phosphorus species
⁄Nitrogen species
⁄Chlorophyll A
›Evaluation
⁄Daily
⁄Duration
⁄Monthly averages
›Match Observed Data to Model Simulation
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Simulated
Observed
Daily
Monthly
Duration
Dev EIA
6%
Dev
18%
Manured
Crop
8%
Unmanured
Grain
11%Soybeans
18%
Other Crops
11%
Pasture Hay
9%
Grassland
9%
Forest
4%
Wetlands
5%
Point Source
0%
Septics
0%Boundary
1%
TSS [ton]
Water Quality Preview
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Dev EIA
7%
Dev
13%
Manured
Crop
4%
Unmanured
Grain
6%
Soybeans
11%
Other Crops
5%Pasture Hay
4%
Grassland
5%
Forest
16%
Wetlands
17%
Point Source
3%
Septics
0%
Boundary
9%
Flow [ac-ft]
0.0
100.0
200.0
300.0
400.0
500.0
600.0
TSS [lbs/acre]
Water Quality Preview
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›Begin with sediment and temperature calibration
⁄Many processes are temperature dependent
⁄N and P associated sediment
Water Quality Preview
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Water Quality Preview
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Water Quality Preview - EXAMPLE TABLE
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Constituent
Primary and Secondary
Calibration Reaches
Primary Calibration
Reaches
Obs Sim Diff Obs Sim Diff
(mg/L)(mg/L)%(mg/L)(mg/L)%
Total Suspended Sediment 25 10 –61 8.1 8.7 7.5
Temperature 68 64 –4.9 54.7 52.2 –4.6
Dissolved Oxygen 7.7 7.2 –7.1 10.5 9.5 –8.9
Total Nitrogen 0.77 0.78 2.1 0.81 0.79 –2.3
Total Inorganic Nitrogen 0.46 0.51 10 0.47 0.49 4.9
Total Kjeldahl Nitrogen 0.37 0.35 –7.3 0.37 0.34 –6.1
Ammonia as N 0.060 0.051 –14 0.033 0.051 56
Nitrite-Nitrate as N 0.40 0.46 14 0.44 0.44 2
Total Phosphorus 0.046 0.038 –17 0.042 0.045 8.3
Orthophosphate as P 0.019 0.016 –15 0.020 0.017 –14
Chorlophyll a 4.7 6.1 29 5.2 6.4 23
Biochemical Oxygen Demand 1.10 0.78 –30 1.2 0.8 –31
Total Organic Carbon 6.5 6.9 6.1 7.0 6.2 –12
SCENARIO APPLICATION MANAGER (SAM)
›Stand Alone Program with GIS Mapping
›HSPF Modeling Experience not Required
›Requires
⁄Calibrated HSPF model
⁄GIS watersheds linked to model
›Will be Used For
⁄Transport and Delivery Factor Development
⁄Existing Conditions Analysis
⁄What-if Scenarios
Scenario Application Manager (SAM)
›Determine Pollutants of Concern
›Identify Critical Locations and Sources
›Develop Custom or Optimized Scenarios
›Scenario Analysis
›Reporting for Documentation
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SAM
Easy as 1-2-3
Transport Factor Calculation Example
›Modeled years are 2004 – 2022
⁄Export Local Loads
▪Local Runoff Loads Delivered to Nearest Stream
▪Aggregate Timestep (Min Daily)
▪Unique Source and Basin
⁄Export Transported Loads
▪Loads Delivered To Selected Outlet
▪Same Timestep, Sources, and Basins
⁄Transport Factors
▪Transported Load / Local Load
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Determine Pollutants of Concern
Identify Critical Locations/Sources
load Concentration
Identify Critical Locations/Sources
Customize Scenario
Customize Scenario
Optimizing
scenarios
$250,000
Prioritize
Subbasins
Target
BMPs
Set Optimization Targets
Optimization Seeks
to Achieve Target
But is Limited by
Available Budget1
2
3
Process Options4
Optimized BMP outputs5
Scenario Analysis
Training and Facilitation of Watershed Planning
›12 Trainings in Past 2 Years
Documentation
›Model Selection Memo - Complete
›QAPP - Complete
› Input Dataset and Simulation Plan - Complete
›Final Model Report (Including Model Calibration Results) – In Progress
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Next Steps and Remaining Timeline
›RESPEC
⁄Develop SAM and Draft Water Quality Calibration (Early January)
⁄Training – January 17th (HSPF) and 18th (SAM)
⁄Finalize Water Quality Calibration (Early March)
⁄Finalize Report (Early March)
⁄Final Stakeholder Meeting (March)
⁄Deliver Model (Late March or Early April)
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Thank you!
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Seth.Kenner@RESPEC.com
Cindie.Kirby@respec.com
Chris.Lupo@respec.com
Project Website:
https://www.deq.nc.gov/about/divisions/water-
resources/water-planning/modeling-assessment/special-
studies#NeuseWatershedModel-12492