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Feb 24, 2022

Index for Total Maximum Daily Load Development and Implementation

Publication: Total Maximum Daily Load Development and Implementation: Models, Methods, and Resources

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Note: Page numbers followed by f and t indicate figures and tables.
abbreviations
389–394
advanced along track scanning radiometer (AATSR)
204
Advanced Microwave Scanning Radiometer for EOS (AMSR-E)
204
Advanced Microwave Sounding Unit (AMSU)
204
Advanced Spaceborne Thermal Emission and Reflection Radiometer (ASTER)
389
Advanced Synthetic Aperture Radar (ASAR)
204
Advanced Topographic Laser Altimeter System (ATLAS)
208
aerial imaging platforms
205. See also remote sensing
agricultural nonpoint-source (AGNPS)
33–34, 389. See also watershed models
Agricultural Research Service (ARS)
33, 389
agricultural runoff management (ARM)
38. See also watershed models
airborne prism experiment (APEX)
207
airborne visible/infrared spectrometer (AVIRIS)
207, 389
airborne visible/infrared spectrometer-next generation (AVIRIS-NG)
207
Alabama Department of Environmental Management (ADEM)
121, 348, 389
Analysis Ready Data (ARD)
206
annualized agricultural nonpoint-source (AnnAGNPS)
33–34, 389. See also watershed models
Aqua Earth-observing satellite
204. See also remote sensing
ArcView combined with SWAT (AVSWAT)
389
ArcView generalized watershed loading function (AVGWLF)
37, 358, 389
ArcView Soil and Water Assessment Tool (ArcSWAT)
41
areal nonpoint-source watershed environment response simulation (ANSWERS)
34–35, 389. See also watershed models
Assessment and Total Maximum Daily Load Tracking and Implementation System (ATTAINS)
279, 308, 389
assimilative capacity
383
Atmospheric InfraRed Sounder (AIRS)
204
Automated Geospatial Watershed Assessment (AGWA)
201
Bacteria Loading Estimator Spreadsheet Tool (BLEST)
159
BASINS modeling system
108
BASINS model releases
109
BASINS utilities
115t–116t
data and supported models in
109, 112
key BASINS components
110t–111t
models and model descriptions in
113t–114t
state-of-the-practice
130. See also integrated modeling systems
BATHTUB model
155–156. See also simple models and methods
Bayesian inference methods
284
Bayesian Monte Carlo (BMC)
276, 389
Bayesian Monte Carlo analysis
289
advantage of
289
cumulative distribution function
292
implementation of
290
likelihood function
292
model outputs to observations and modeling errors
290
posterior distributions
291
probability density function
292. See also model uncertainty analysis
beneficial/designated uses
383
best management practices (BMPs)
3, 200, 357, 383, 389
Better Assessment Science Integrating Point and Nonpoint Sources (BASINS)
7, 38, 108, 201, 222, 389. See also BASINS modeling system;
model calibration and validation
biochemical oxygen demand (BOD)
44, 383, 389
breakpoint rainfall
383
Calculation of Percent (PCT)
392
calibration
383
California Department of Water Resources (CDWR)
389
California Environmental Protection Agency (CEPA)
390
Carbonaceous Biochemical Oxygen Demand (CBOD)
389
cascade of planes in two-dimensional (CASC2D)
36, 389
Center for Computational Hydroscience and Engineering (CCHE)
389
Center for Computational Hydroscience and Engineering-1D/2D/3D (CCHE-1D/2D/3D)
96, 389
applicability to total maximum daily load studies
97
model background and capabilities
96. See also receiving water quality models
Center for Exposure Assessment Modeling (CEAM)
335, 390
Central Valley Water Board (CVWB)
390
CE-Qual-W2
390
applicability to total maximum daily load studies
94
model
93f
model background and capabilities
93–94. See also receiving water quality models
chemical oxygen demand (COD)
33, 390
Chesapeake assessment scenario tool (CAST)
358, 389
Chesapeake Bay marketplace
21–22
Chesapeake Bay Program
10, 180, 367. See also state or watershed-specific models
Chesapeake Bay TMDL
359. See also TMDL implementation modeling
chlorophyll-a (Chl-a)
348, 390
Clean Water Act (CWA)
1, 332, 383–384, 390
Clean Water State Revolving Fund
6
climate assessment tool (CAT)
112, 389
Clouds and Earth's radiant energy system (CERES)
204
Code of Federal Regulations (CFR)
2
coefficients of variation (CVs)
287
combined sewer overflows (CSOs)
369
community multi-scale air quality (CMAQ)
118, 390
compact airborne spectrographic imager (CASI)
207
complex water control structures
44
confirmation or corroborative testing
384
Consortium of Universities for the Advancement of Hydrologic Science (CUAHSI)
217
contaminants
85
emerging
333
continuous simulation method
178. See also critical condition
conversion of units
379t–381t
Corps of Engineers Integrated Compartment Water Quality Model (CE-QUAL-ICM)
89, 90f
applicability to total maximum daily load studies
90
features of
89
model background and capabilities
89. See also receiving water quality models
critical condition
169, 384
Chesapeake Bay Program
180
Chesapeake Bay TMDL
179
comparison of available methods
173t–175t
continuous simulation method
178
critical flow-storm approach
183–186
determination
169, 186
dynamic continuous simulation models to analyze impairment
177–180
load–duration curves
181–183
methodology for
171
7Q10
170, 172
specific critical conditions
170
state-of-the-art and state-of-the-practice
187–188
steady-state models to analyze impairment
172, 176–177
TMDL development examples
176
USEPA's water quality criteria
170, 177
critical flow storm (CFS)
171, 183–186, 390. See also critical condition
cumulative distribution function (CDF)
292
curve number (CN)
136, 390
customary units
379t–381t
Danish Hydraulic Institute (DHI)
40, 100
data management
221. See also model calibration and validation
decision support system (DSS)
308, 390
Decision Support Tool (DST)
390
Delaware Department of Natural Resources and Environmental Control (DNREC)
390
Delaware River Basin Commission (DRBC)
390
Department of Natural Resources (DNR)
390
designated use (DU)
384, 387, 390
digital elevation model (DEM)
42
digital elevation processing software
202
dissolved oxygen (DO)
120, 175, 201, 216, 384, 390
dissolved phosphorus (DP)
390
Distributed Hydrology Soil Vegetation Model (DHSVM)
390
distribution testing
251. See also model calibration and validation
Doppler Orbitography and Radiopositioning Integrated by Satellite (DORIS)
204
dynamic continuous simulation models
177–180. See also critical condition
Dynamic One-Dimensional River Model by Georgia Environmental Protection Division (EPD-RIV1)
390
Dynamic Reservoir Simulation Model (DYRESM)
390
Dynamic Reservoir Simulation Model-Water Quality (DYRESM-WQ)
390
dynamic watershed simulation model (DWSM)
35–36, 390. See also watershed models
ECOLAB
41. See also watershed models
Electric Power Research Institute (EPRI)
45
Engineer Research and Development Center (ERDC)
89, 116
Ensemble Kalman filter (EnKF)
296. See also model uncertainty analysis
Environmental and Water Resources Institute (EWRI)
390
Environmental Fluid Dynamics Code (EFDC)
91, 120, 330, 390
applicability to total maximum daily load studies
92–93
model background and capabilities
91–92
water quality model
92. See also receiving water quality models
Environmental Protection Agency (EPA)
390
Environmental Protection Division (EPD)
97, 390
Environmental Protection Division-RIV1 (EPD-RIV1)
97
applicability to total maximum daily load studies
97–98
model background and capabilities
97. See also receiving water quality models
Environmental Systems Research Institute (ESRI)
109, 390
eutrophication processes
87
evapotranspiration (ET)
209
Everglades agricultural area model (EAAMOD)
44
Extended Kalman Filter (EKF)
296. See also model uncertainty analysis
Fecal Coliform (FC)
390
Federal Water Pollution Control Act Amendments of 1972
4
first-order error analysis (FOEA)
276, 390
first-order variance analysis (FOVA)
278, 286–288, 390
coefficients of variation
287
dimensionless sensitivity coefficients
287
implementation of
287–288. See also model uncertainty analysis
Fish and Wildlife (F&W)
390
Flow–Duration Curve (FDC)
390
Generalized Likelihood Uncertainty Estimation (GLUE)
284, 390
generalized watershed loading function (GWLF)
37, 109, 154, 358, 390
AVGWLF
155
GWLF-E
367. See also watershed models
geographical information system (GIS)
109, 154, 201, 367, 390
advantages of using
155
applications in total maximum daily load modeling
208–210
dataset sources
202
geodatabase
371–372
platforms
202
proprietary software modeling frameworks
202
software for digital elevation processing
202
spatial modeling of data
203
state-of-the-art and state-of-the-practice
210
water resource model interfaces
210
workflow models
154–155. See also model data
remote sensing
simple models and methods
state or watershed-specific models
Global Ozone Monitoring by Occultation of Stars (GOMOS)
204
graphical user interface (GUI)
59, 91, 390
Gravity Recovery and Climate Experiment (GRACE)
208
gridded surface and subsurface hydrologic analysis (GSSHA)
36–37, 116, 390. See also watershed models
groundwater loading effects of agricultural management systems (GLEAMS)
44. See also watershed models
Growing Season Average (GSA)
390
HEC Center–Data Storage System (HEC-DSS)
222, 391. See also model calibration and validation
HEC-Hydrologic Modeling System (HEC-HMS)
222
HEC-River Analysis System (HEC-RAS)
222
HSPF enhanced expert system (HSPEXP+)
254, 391
Humidity Sounder for Brazil (HSB)
204
hydraulic structures
94
hydrodynamic models
91, 129. See also CE-Qual-W2
Hydrological Simulation Program-FORTRAN (HSPF)
38–39, 118, 127, 179. See also watershed models
Hydrologic Engineering Center (HEC)
94, 222, 391
Hydrologic Engineering Center-Hydrologic Modeling System (HEC-HMS)
37–38, 391. See also watershed models
Hydrologic Engineering Center-River Analysis System (HEC-RAS)
94, 391
applicability to total maximum daily load studies
96
model background and capabilities
94
nutrient simulation modules in
95f. See also receiving water quality models
hydrologic modeling
38. See also watershed models
hydrologic response units (HRUs)
42
Hydrologic Simulation Program-FORTRAN (HSPF)
222, 391
hyperspectral remote sensing imagery
207–208. See also remote sensing
hyperspectral sensors
207. See also remote sensing
hypothesis testing
251, 253. See also model calibration and validation
Ice, Cloud, and land Elevation Satellite 2 (ICESAT-2)
208
ICM. See Corps of Engineers Integrated Compartment Water Quality Model
Idaho Department of Environmental Quality (IDEQ)
391
impairment
384
implementation modeling
384
implementation plan
384
importance sampling (IS)
284, 391
information/results
384
infrared (IR)
203, 391
inherent optical properties (IOP)
207
Integrated Compliance Information System (ICIS)
217
integrated hydrological model (IHM)
117, 391
Integrated Lake-Watershed Acidification Study (ILWAS)
45
integrated modeling systems
107, 108, 128–129, 384
BASINS modeling system
108–112
performance evaluations of
126–128
state-of-the-art and state-of-the-practice
129
watershed modeling system
112, 116–117. See also linked models
integrated parameter estimation and uncertainty analysis tool plus (IPEAT+)
254
Iowa Department of Natural Resources (IDNR)
391
jurisdictional agency
384
Kalman filtering (KF)
295–296. See also model uncertainty analysis
kinematic runoff and erosion (KINEROS)
39–40, 391. See also watershed models
Kling–Gupta efficiency (KGE)
250
land use/land cover (LULC)
193, 216, 391
Laterally Averaged Reservoir Model (LARM)
391
Latin hypercube sampling (LHS)
289, 391
leave-one-out (LOO)
255
light detection and ranging (LiDAR)
206, 391. See also remote sensing
linkages
107–108. See also linked models
linked models
107, 117, 128–129
in Chesapeake Bay total maximum daily load
118–120
HSPF, UnTRIM, and CE-QUAL-ICM applied to Lynnhaven river watershed
122–126, 127t
LSPC-EFDC-WASP models applied to Saugahatchee Creek watershed
120–122
performance evaluations of
126–128
state-of-the-art and state-of-the-practice
129. See also integrated modeling systems
Little Hoover Commission (LHC)
333, 391
load allocation (LA)
385, 391
load capacity (LC)
273, 391
load–duration curve (LDC)
157–159, 171, 181–183, 391. See also critical condition
simple models and methods
LOAD ESTimator (LOADEST)
149–150, 200. See also simple models and methods
Loading Simulation Program C (LSPC)
222
Loading Simulation Program in C++ (LSPC)
40, 120, 391. See also watershed models
Long-Term Hydrologic Impact Analysis (L-THIA)
151–152. See also simple models and methods
low-impact development (LID)
43, 152, 375
management objectives constrained analysis of uncertainty (MOCAU)
284, 391
management practices
385
MapWindow Soil and Water Assessment Tool (MWSWAT)
41
margin of safety (MOS)
201, 271, 385, 391
determination in case-study TMDL
279
estimation of
274–278, 277f
explicit
274–275
implicit
275–276
risk-based
276–278
risk-based approaches for estimating TMDL
278
state-of-the-art and state-of-the-practice
296–298
survey of MOS methods in sampled TMDL reports
280t–283t
total maximum daily load
273–274. See also model uncertainty analysis
Markov chain Monte Carlo (MCMC)
284, 294, 391
formulation of likelihood function
295
Metropolis algorithm
294
Metropolis–Hastings algorithm
294
SCEM-UA algorithm
294. See also model uncertainty analysis
Maryland Phase I Watershed Implementation Plan
360. See also TMDL implementation modeling
maximum likelihood estimation (MLE)
149
mean absolute error (MAE)
250, 391
mean squared error (MSE)
250
measurements of pollution in the troposphere (MOPITT)
204
medium resolution imaging spectrometer (MERIS)
204
Metropolis algorithm
294. See also Markov chain Monte Carlo
Metropolis–Hastings algorithm
294. See also Markov chain Monte Carlo
Metropolitan Washington Council of Governments (MWCOG)
391
Michelson Interferometer for Passive Atmospheric Sounding (MIPAS)
204
Microsoft (MS)
146
microwave (MW)
203, 391
microwave radiometers (MWRs)
203
MIKE 11
100. See also receiving water quality models
Mike Systém Hydrologique Européen (MIKE SHE)
40–41, 391. See also watershed models
million gal. per day (MGD)
348, 391
Ministry of Economy, Trade, and Industry (METI)
391
Minnesota Pollution Control Agency (MPCA)
391
MINTEQA2
98–99. See also receiving water quality models
model
385
model calibration and validation
215
alternate measures of global fit
250–251
automatic calibration combining manual analysis
254
bacteria-specific guidelines for model evaluation
252
BASINS
222
data management
221–222
data sources for setup, calibration, and validation
218t–220t
distribution testing
251
efficient adaptive techniques
254
evaluation criteria for model performance
255–260
global sensitivity analysis
260
goodness-of-fit measures
245t–249t, 251
HEC-DSS
222
hypothesis testing
251, 253
limitations on goodness-of-fit measures
252–253
manual and automatic calibration
253–254
model data and sources of data
216–221
model performance criteria based on coefficient of determination
257t
model performance criteria based on Nash–Sutcliffe Efficiency
258t
model performance criteria based on percent bias
259t
model performance criteria for bacteria/toxic modeling
260t
model performance criteria for daily and monthly timescales
256t
optimization algorithm
254
parameterization
224–226, 244, 250–253
performance grading
256
precalibration
222–224
principal parameters for hydrologic calibration
227t–235t
principal parameters for water quality calibration
236t–243t
simulation reliability determination
251
state-of-the-art and state-of-the-practice
260–261
statistics for watershed modeling
250–251
synoptic data collection
221
three-tiered hierarchy of validation proposed
255
validation
254–255
WRDB
222
model data
193
data requirements for running TMDL models
198t–199t
data requirements for TMDL model setup
196t–197t
discrete data
195
LOADSET
200
model parameter values
194–200
parameterizing
194
system data
195
total maximum daily load data resources
200–201
types of
193–194. See also geographical information system
remote sensing
model skill score (MSS)
250, 337, 338
model uncertainty analysis
271
applied in water quality modeling studies
285t–286t
Bayesian Monte Carlo analysis
289–292
first-order variance analysis
286–288
Generalized Likelihood Uncertainty Estimation Method
293–294
Kalman filtering
295–296
Markov Chain Monte Carlo method
294–295
methods
279, 284–296
Monte Carlo method
288–289
state-of-the-art and state-of-the-practice
296–298
SUFI-2
284
uncertainty
271
in watershed modeling
284. See also margin of safety
moderate resolution imaging spectroradiometer (MODIS)
204
modifications of USLE (MUSLE)
148
monitoring
385
Montana Department of Environmental Quality (MDEQ)
391
Monte Carlo (MC)
278, 288–289, 391
simulation
385. See also model uncertainty analysis
Multiple-response Bayesian calibration (MRBC)
391
multispectral remote sensing imagery
206–207. See also remote sensing
multispectral sensors
207. See also remote sensing
Municipality Separate Storm Sewer System (MS4)
368, 391
Nash–Sutcliffe efficiency (NSE)
119, 128, 129, 130, 250, 337, 392
National Aeronautics and Space Administration (NASA)
391
National Agricultural Statistics Service (NASS)
221, 391
National Center for Computational Hydroscience and Engineering (NCCHE)
392
National Centers for Environmental Information (NCEI)
392
National Climatic Data Center (NCDC)
392
National Elevation Dataset (NED)
392
National Estuarine Research Reserves System (NERRS)
392
National Flood Frequency Program (NFF)
116
National Flood Insurance Program (NFIP)
43
National Hydrography Dataset (NHD)
109, 392
National Land Cover Dataset (NLCD)
42, 392
National Oceanic and Atmospheric Administration (NOAA)
392
National Pollutant Discharge Elimination System (NPDES)
2, 319, 392
National Research Council (NRC)
8, 392
National Resource Conservation Council (NRCS)
392
National Streamflow Statistics Program
181
National Water Information System (NWIS)
392
Nationwide Urban Runoff Program (NURP)
143, 144, 392
Natural Condition (NC)
391
Natural Resources Conservation Service (NRCS)
33, 148, 226, 342, 385
Naval Air Station Oceana (NAS Oceana)
124
Nevada Division of Environmental Protection (NVDEP)
392
New Mexico Environment Department (NMED)
392
Nitrogen-Ammonia (NH3-N)
392
Nitrogen Phosphorus Potassium and Zooplankton (NPK-Z)
392
nonlinked complex models
127
nonpoint-source (NPS)
2, 38, 195, 392
contaminant load
85
pollution
385. See also watershed models
nonstructural stormwater management solutions
359
normalized root-mean squared error (NRMSE)
250, 392
Ohio Environmental Protection Agency (OEPA)
392
One-Dimensional Transport with Equilibrium Chemistry (OTEQ)
99, 392
applicability to total maximum daily load studies
100
model background and capabilities
99. See also receiving water quality models
Oregon Department of Environmental Quality (ODEQ)
330, 392
organic enrichment (OE)
121, 392
organic nitrogen (ON)
121
organic phosphorus (OP)
121
orthophotography
209
Pacific Northwest Laboratory (PNL)
392
Parameter-elevation Regressions on Independent Slopes Model (PRISM)
392
parameter estimation (PEST)
254, 392. See also model calibration and validation
Parameter ESTimation and uncertainty analysis (PEST)
39, 340
Pearson's product-moment correlation coefficient
250
Pennsylvania Department of Environmental Protection (PADEP)
367. See also state or watershed-specific models
Percent Bias (PBIAS)
392
percent error (PE)
250, 392
Performance Evaluation Criteria (PEC)
128, 392
Performance Measure (PM)
392
periphyton
329
permit
385
Permit Compliance System (PCS)
217, 392
Permit Condition (PC)
392
point source (PS)
2, 195, 392
contaminant load
85
solution
386
pollutant
359–361, 386
load
158
-removal mechanisms
360
sources
146, 359–361. See also TMDL implementation modeling
polychlorinated biphenyl (PCB)
251, 392
portable remote imaging spectrometer (PRISM)
207, 207
Portland State University (PSU)
93
posterior parameter distributions (PPDs)
278
potential evapotranspiration (PET)
34, 392
Prediction of Worldwide Energy Resources (POWER)
392
predictions from observations is percent bias (PBIAS)
250
probabilistic collocation method (PCM)
284, 392
probabilistic methods
290
probability density function (PDF)
292
process/mechanism
386
Public Water Supply (PWS)
392
QGIS Interface for SWAT (QSWAT)
210
QUAL2K
98. See also receiving water quality models
quality assurance (QA)
222
quality assurance project plan (QAPP)
255, 392
Ratio of Root Mean Squared Error and standard deviation of observed data (RSR)
393
receiving water quality models
85, 320
advances in
345
causes of impairment
86t
Center for Computational Hydroscience and Engineering-1D/2D/3D
96–97
CE-QUAL-W2 model
93–94
contaminants
85
Corps of Engineers Integrated Compartment Water Quality Model
89–90
Environmental Fluid Dynamics Code
91–93
Environmental Protection Division-RIV1
97–98
Hydrologic Engineering Center-River Analysis System
94–96, 95f
linkage between watershed, hydrodynamic, and water quality models
87f
MIKE 11
100
MINTEQA2 and Visual MINTEQ
98–99
nonpoint-source contaminant load
85
One-Dimensional Transport with Equilibrium Chemistry
99–100
point source contaminant load
85
QUAL2K
98
selected receiving waterbody models
88t
state-of-the-art and state-of-the-practice
100–101
for total maximum daily load applications
89
Water Quality Analysis Simulation Program
90–91
watershed model
85
receiving waters/receiving waterbodies
386
Red Alert 2 (RA-2)
204
Regionalized Sensitivity Analysis (RSA)
393
remote sensing
203
aerial imaging platforms
205
applications in total maximum daily load modeling
208–210
Aqua Earth-observing satellite
204
derived water surface data
209
hyperspectral remote sensing imagery
207–208
hyperspectral sensors
207
light detection and ranging
206
multispectral remote sensing imagery
206–207
multispectral sensors
207
platforms
206
processing and error-correcting satellite imagery
205
satellite and aerial imagery
205
satellites
204
specialized platforms
208
state-of-the-art and state-of-the-practice
210. See also geographical information system
model data
residential waste management systems
333
Revised Universal Soil Loss Equation (RUSLE)
393
Revised Universal Soil Loss Equation 2 (RUSLE2)
136, 147–149, 393. See also simple models and methods
root-mean-squared error (RMSE)
129, 250, 393
Royal Institute of Technology in Stockholm, Sweden (KTH)
391
sanitary sewer overflows (SSOs)
122–123, 369
San Joaquin River Input–Output (SJRIO)
153–154, 393
satellite
204
and aerial imagery
205. See also remote sensing
Scanning Imaging Absorption SpectroMeter for Atmospheric CHartography (SCIAMACHY)
204
SCEM-UA algorithm
294. See also Markov chain Monte Carlo
Sea-viewing Wide Fieldof-view Sensor (SeaWiFS)
207
Sentinel-3 Ocean and Land Color Instrument (OLCI)
207
sequential uncertainty fitting (SUFI-2)
284
7Q10
170, 172, 385
Shuffled Complex Evolutionary (SCE)
393
Shuttle Radar Topography Mission (SRTM)
393
simple method to estimate urban stormwater loads
143–145. See also simple models and methods
simple models and methods
135, 159–160
BATHTUB model
155–156
comparison in TMDL determination
138t–142t
geographical information system workflow models
154–155
load–duration curve
157–159
LOAD ESTimator
149–150
Long-Term Hydrologic Impact Analysis
151–152
Nationwide Urban Runoff Program
143, 144
review of
136
Revised Universal Soil Loss Equation 2
147–149
simple method to estimate urban stormwater loads
143–145
simple receiving water models and methods
155
simple transient mass balance models
152–154
simple watershed models and methods
137
simplified mass balances
137, 143
spatially referenced regressions on watershed attributes
150–151
Spreadsheet Tool for the Estimation of Pollutant Load
146–147
state-of-the-art and state-of-the-practice
160–161
Stream Segment Temperature model
156–157
Watershed Treatment Model
145–146
simple transient mass balance models
152–154. See also simple models and methods
simplified mass balances
137, 143. See also simple models and methods
SI units
379t–381t
Soil and Water Assessment Tool (SWAT)
41–43, 109, 202, 284, 393. See also watershed models
Soil and Water Engineering Technology (SWET)
44. See also watershed models
Soil Conservation Service (SCS)
385–386, 393
Soil Survey Geographic (SSURGO)
42, 393
Source Loading and Management Model for Windows (WinSLAMM)
358, 368, 394
South Carolina Department of Health and Environmental Control (SCDHEC)
158, 393
Spatially Referenced Regressions on Watershed Attributes (SPARROW)
150–151, 393. See also simple models and methods
spreadsheet analysis
368–369. See also state or watershed-specific models
spreadsheet tool for estimating pollutant load (STEPL)
33, 216, 146–147, 358, 370–371, 393. See also simple models and methods;
state or watershed-specific models
stakeholders
357
state
386
state or watershed-specific models
362, 367
Chesapeake Bay Program
367
custom modeling using GIS geodatabase
371–372
GIS tools and associated geodatabases
371
Pennsylvania Department of Environmental Protection
367
pollutant loading
369
spreadsheet analysis
368–369
spreadsheet tool for estimating pollutant load
370–371
Watershed Treatment Model
369–370
Wisconsin Department of Natural Resources
368. See also TMDL implementation modeling
State Soil Geographic (STATSGO)
42, 393
State Water Pollution Control Revolving Fund
Clean Water State Revolving Fund
steady-state models
172, 176–177, 386. See also critical condition
stochastic analysis of model residuals (SAMR)
284, 393
Storage and Retrieval and Water Quality Exchange (STORET-WQX)
393
stormwater: best management practice pollutant control
359
treatment methods
360. See also TMDL implementation modeling
storm water management model (SWMM)
43–44, 109, 202, 359, 393. See also watershed models
Stream Network Temperature (SNTEMP)
156, 393
Stream Segment Temperature (SSTEMP)
156–157, 393. See also simple models and methods
Surface Water Statistics (SWSTAT)
393
SWAT calibration and uncertainty programs (SWAT-CUP)
254, 393
symbols
395–401
synoptic data
386
collection
221. See also model calibration and validation
synthetic aperture radar (SAR)
203
Terrain Analysis Using Digital Elevation Models (TAUDEM)
202, 393
TMDL (Total maximum daily load)
1, 31, 85, 107, 271, 357, 386, 393
allocation
13–14
amendments to CWA
4–9
analysis models
319, 320
approach
1–10
benefits of total maximum daily load approach
21–22
Chesapeake Bay Program
10
Clean Water State Revolving Fund
6
determination
13
development modeling
208
document
1–2
Federal Water Pollution Control Act Amendments of 1972
4
history of TMDL approach to water quality–based management
4
identification
12–13
implementation planning and compliance
14
Manual of Practice
22–23
maximum allowable pollutant load
2
modeling required to determine
19–21
multijurisdictional
3
multiple
3
procedure for determination, allocation, and implementation planning
12
process of determining
10
risk-based approaches for estimating
278
state, territory, & authorized tribe TMDL determination, allocation, and implementation
11f
synoptic and monitoring data requirements
14, 19
TMDL-DB
310f
TMDL model development workflow
313–315
TMDL reports
308–309, 312
Water Pollution Control Act of 1948
4
water quality variables and modeling objectives
15t–18t
watershed-scale TMDL approach
3
TMDL-DB (total maximum daily load database)
309, 310f, 319, 393
model selection and applications for
319
TMDL implementation modeling
357, 372–374
availability and support
362
Chesapeake Bay Program
367
Chesapeake Bay TMDL
359
choice of models for
358–362
data resources for modeling
361
expertise and access
361–362
GIS tools and geodatabases
371
Locust Fork and Village Creek TMDL load-reduction scenarios
349t–350t
Maryland Phase I Watershed Implementation Plan
360
modeling using GIS geodatabase
371–372
models for implementation
362–372
overall approach to
358
Pennsylvania Department of Environmental Protection
367
planning case study
348–351
pollutant loading
369
pollutant-removal mechanisms
360
range of pollutants and pollutant sources
359–361
spreadsheet analysis
368–369
spreadsheet tool for pollutant load
370–371
stakeholders
357
state-of-the-art and state-of-the-practice
374–375
stormwater best management practice pollutant control
359
stormwater treatment methods
360
structure and capabilities of selected implementation models
363t–365t
treatment practices for selected implementation models
366t
watershed-specific models
362–372
Watershed Treatment Model
369–370
ways to carry out that TMDL implementation
373
Wisconsin Department of Natural Resources
368
TMDL modeling
169, 319
advances in receiving water quality model
345
Bayesian hypothesis testing
328
characteristics of impaired waterbody
329
choice of appropriate TMDL model
319
to determine, allocate, and implement TMDL
341–343
dimensionless MSS
338
dimensionless Nash–Sutcliffe efficiency
337
fundamental model selection principles
326–328
future innovation in
343–346
hypothesis testing
327
model evaluation, calibration–validation, and uncertainty estimation
334–341
models and methods for TMDL determination
321–323
models available for TMDL analysis
320
model selection
323–334
models in TMDL analysis
319
model uncertainty estimation
341
new automated calibration methods
340
performance evaluation
336–339
performance measures for qualitative assessment
339–340
principles for selection of TMDL models
326
scientific basis for structured holistic model selection process
320
stakeholder and expert engagements
332–334
stakeholder engagement
333
state-of-the-art and state-of-the-practice
346–348
synoptic data collection
331
technical and practical considerations in model selection
328–332
TMDL implementation planning case study
348–351
TMDL model selection
319, 324f
updates to models
344
USEPA approval process for TMDL document
335
WARMF model
345
water quality management document
336
watershed model extensions
344. See also critical condition
TMDL model performance evaluation
334, 336–337
dimensionless MSS
338
dimensionless Nash–Sutcliffe efficiency
337
measures for qualitative assessment
339–340
during model calibration and validation
338–339
model calibration, validation, and sensitivity analysis
340–341
during model selection
337–338
model uncertainty estimation
341
new automated calibration methods
340
USEPA approval process for TMDL document
335
water quality management document
336. See also TMDL modeling
TMDL model selection
323
Bayesian hypothesis testing
328
characteristics of impaired waterbody
329
flowchart
324f
hypothesis testing
327
performance evaluation during
337–338
principles
326–328
scientific basis for structured holistic
320
stakeholder and expert engagements
332–334
stakeholder engagement
333
synoptic data collection
331
technical and practical considerations
328–332. See also TMDL modeling
TMDL Report Selection (TRS) tool
73, 309, 311, 393
frequency count of models cited in
315f
model frequency statistics in output produced by
313f
steps to acquire data from ATTAINS database
311f
TMDL model development workflow using
313–315
use of
309–315
user interface
316f
version 1. 2
313, 316f. See also USEPA TMDL report archive and report search tool
TMDL TC (Total Maximum Daily Load Analysis and Modeling Technical Committee)
393
topographic parameterization (TOPAZ)
202, 393
Total Dissolved Solids (TDS)
393
total Kjeldahl nitrogen (TKN)
126, 393
Total Nitrogen (TN)
393
total phosphorus (TP)
122, 126, 393
total suspended solids (TSS)
177, 393
triangular irregular networks (TINs)
116
two-dimensional (2D)
93
integrated hydrology
116
Two-Phase Monte Carlo (TPMC)
393
ultimate carbonaceous biochemical oxygen demand (CBODu)
121
uncertainty
271
aleatory
272
epistemic
272–273
United States Army Corps of Engineers (USACE)
89, 155, 222, 336, 362, 393
United States Department of Agriculture (USDA)
393
United States Environmental Protection Agency (USEPA)
308, 386, 393
water quality criteria
170, 177
United States Geological Survey (USGS)
150, 172, 386, 393
universal soil loss equation (USLE)
37, 370, 394
UnTRIM (Unstructured Tidal, Residual, and Intertidal Mudflat)
123
Urban Catchment Model P-8
368
USEPA TMDL report archive and report search tool
307
acceptable TMDL
309
accessing TMDL database and use of TRS tool
309–315
conservative constraints
307
features of TMDL report selection tool
311–312
frequency counts for constituents appearing in TMDL reports
314f
model frequency statistics in output produced by TRS tool
313f
state-of-the-art and state-of-the-practice
315–317
steps to acquire data from ATTAINS database for analysis using TRS tool
311f
TMDL-DB
310f
TMDL model development workflow
313–315
TMDL reports
308–309
TMDL report summary statistics
312
TRS tool
311
TRS tool output cited in TMDL reports
315f
TRS tool user interface
316f
USEPA ATTAINS database
308, 309–310
Utah Department of Environmental Quality (UDEQ)
393
Virginia Department of Environmental Quality (VDEQ)
126, 179, 394
Virginia Institute of Marine Science (VIMS)
123
Visible (VIS)
203, 394
Visual Basic (VB)
146
Visual MINTEQ
98–99. See also receiving water quality models
WARMF model
345. See also TMDL modeling
waste assimilative capacity
386–387
Waste Load Allocation (WLA)
97, 177, 274, 387, 394
Wastewater Treatment Plant (WWTP)
394
Water Analysis Simulation Program (WASP)
394
waterbody
1, 387
Water Information System KISTERS (WISKI)
222, 394
Water Pollution Control Act of 1948
4
water quality (WQ)
74
parameter
387
standard
387
water quality analysis simulation program (WASP)
90–91, 109, 120, 222. See also receiving water quality models
Water Quality Model and Sediment Transport Model (WQSTM)
119
Water Quality Portal (WQP)
217, 394
Water Resources Database (WRDB)
97, 222, 394. See also model calibration and validation
watershed
35, 387
loading models
127, 129
management programs
4
model
85
model extensions
344. See also receiving water quality models
TMDL modeling
Watershed Analysis Risk Management Framework (WARMF)
45, 201, 394. See also watershed models
watershed assessment model (WAM)
33, 44–45, 109, 216. See also watershed models
Watershed Boundary Dataset (WBD)
394
Watershed Data Management (WDM)
38. See also watershed models
watershed data management utilities (WDMutil)
109, 394
Watershed Implementation Plan (WIP)
387
Watershed Management Technical Committee (WMTC)
394
watershed modeling system (WMS)
36, 108, 112, 394
applications of
117
WMSHydro
116. See also integrated modeling systems
watershed models
watershed models
31, 85, 387
agricultural nonpoint-source
33–34
analyses of models
45
ANSWERS-2000
34–35
channel flow-routing procedure comparison
71f
characteristics and capabilities
46t–48t, 59
continuous models
32
descriptions of selected
33–45
dynamic
35–36
ECOLAB
41
event-based models
31–32
extensions
344
field-scale models
44
formulations in water-quality simulations
53t–58t
generalized watershed loading function
37
gridded surface and subsurface hydrologic analysis
36–37
Hydrological Simulation Program-Fortran
38–39
Hydrologic Engineering Center-Hydrologic Modeling System
37–38
hydrologic modeling
38
hydrologic simulations
69–71
kinematic runoff and erosion
39–40
Loading Simulation Program in C++
40
mathematical bases in models
49t–52t
MIKE Système Hydrologique Européen
40–41
overland runoff routing procedure comparison
70f
raindrop-impacted soil detachment
35
recommendations
74–76
Soil and Water Assessment Tool
41–43
state-of-the-art and state-of-the-practice
76
Storm Water Management Model
43–44
strengths and limitations of models and suitability
60t–68t, 72–74
suitability for TMDL
45
TRS tool
73
types
31
water quality simulations
72
watershed
35
Watershed Analysis Risk Management Framework
45
Watershed Assessment Model
44–45
watershed nonpoint-source models
31
Watershed Treatment Model (WTM)
145–146, 358, 369–370, 394. See also simple models and methods;
state or watershed-specific models;
Wetland Management Simulator WIP: Watershed Implementation Plan (WETMANSIM)
152, 394
Wisconsin Department of Natural Resources (WI DNR)
368. See also state or watershed-specific models
WMSHydro
116

Information & Authors

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Published In

Go to Total Maximum Daily Load Development and Implementation
Total Maximum Daily Load Development and Implementation: Models, Methods, and Resources
Pages: 403 - 419
Editors: Harry X. Zhang, Ph.D., Nigel W.T. Quinn, Ph.D. https://orcid.org/0000-0003-3333-4763, Deva K. Borah, Ph.D. https://orcid.org/0000-0002-2107-9390, and G. Padmanabhan, Ph.D. https://orcid.org/0000-0002-3209-1379
ISBN (Print): 978-0-7844-1594-8
ISBN (Online): 978-0-7844-8382-4

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Published online: Feb 24, 2022
Published in print: Mar 1, 2022

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