Knowledge (XXG)

Stochastic empirical loading and dilution model

Source ๐Ÿ“

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difficult or impossible to obtain because it models the interactions among hydrologic variables (with different probability distributions) that result in a population of values that represent likely long-term outcomes from runoff processes and the potential effects of different mitigation measures. SELDM also provides the means for rapidly doing sensitivity analyses to determine the potential effects of different input assumptions on the risks for water-quality excursions. SELDM produces a population of storm-event and annual values to address the questions about the potential frequency, magnitude, and duration of water-quality excursions. The output represents a collection of random events rather than a time series. Each storm that is generated in SELDM is identified by sequence number and annual-load accounting year. The model generates each storm randomly; there is no serial correlation, and the order of storms does not reflect seasonal patterns. The annual-load accounting years, which are just random collections of events generated with the sum of storm interevent times less than or equal to a year, are used to generate annual highway flows and loads for TMDL analysis and the lake basin analysis.
146:, the upstream-basin characteristics, and, if a lake analysis is selected, the lake-basin characteristics. The hydrologic data include precipitation, streamflow, and runoff-coefficient statistics. The water-quality data include highway-runoff-quality statistics, upstream-water-quality statistics, downstream-water-quality definitions, and BMP-performance statistics. There also is a GUI form for running the model and accessing the distinct set of output files. The SELDM interface is designed to populate the database with data and statistics for the analysis and to specify index variables that are used by the program to query the database when SELDM is run. It is necessary to step through the input forms each time an analysis is run. 155:
precipitation events, and stormflow file. If the Stream Basin or Stream and Lake Basin output options are selected, then the prestorm streamflow and dilution factor files also are created. If these same two output options are selected and, in addition, one or more downstream water-quality pairs are defined by using the water-quality menu, then the upstream water-quality and downstream water-quality output files also are created by SELDM. If the Stream and Lake Basin Output or Lake Basin Output option is selected, and one or more downstream water-quality pairs are defined by using the water-quality menu, then the Lake Analysis output file is created when the Lake Basin Analysis is run. The output files are written as
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calculations for constituents with concentrations of nanograms per liter or picograms per liter and to address other sundry issues. Version 1.1.0 was released in May 2021 to add batch processing, change the highway runoff duration used for upstream transport curves from the discharge duration, which could vary from BMP to BMP, to the runoff-concurrent duration and volume, and fix a problem that allowed users to simulate a dependent variable in a lake analysis without the explanatory variable, which caused an error. Version 1.1.1 was released in December 2022 to make SELDM compatible with the 32- and 64-bit versions of Microsoft Office; this version has the ability to simulate emerging contaminants including
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constituents from National datasets. Input statistics may be selected on the basis of the latitude, longitude, and physical characteristics of the site of interest and the upstream basin. The user also may derive and input statistics for each variable that are specific to a given site of interest or a given area. Information and data from hundreds to thousands of sites across the country were compiled to facilitate use of SELDM. Most of the necessary input data are obtained by defining the location of the site of interest and five simple basin properties. These basin properties are the drainage area, the basin length, the basin slope, the impervious fraction, and the basin development factor
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and a stormwater discharge location that affect the volume, timing, or quality of runoff. SELDM uses a simple stochastic statistical model of BMP performance to develop planning-level estimates of runoff-event characteristics. This statistical approach can be used to represent a single BMP or an assemblage of BMPs. The SELDM BMP-treatment module has provisions for stochastic modeling of three stormwater treatments: volume reduction, hydrograph extension, and water-quality treatment. In SELDM, these three treatment variables are modeled by using the
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upstream receiving stream to calculate flows, concentrations, and loads in the receiving stream downstream of the stormwater outfall. The lake-basin analysis also is a stochastic multi-year mass-balance analysis. The lake-basin analysis uses the highway loads that occur during runoff periods, the total annual loads from the lake basin to calculate annual loads to and from the lake. The lake basin analysis uses the volume of the lake and pollutant-specific attenuation factors to calculate a population of average-annual lake concentrations.
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concentrations. Results are ranked, and plotting positions are calculated, to indicate the level of risk of adverse effects caused by runoff concentrations, flows, and loads on receiving waters by storm and by year. Unlike deterministic hydrologic models, SELDM is not calibrated by changing values of input variables to match a historical record of values. Instead, input values for SELDM are based on site characteristics and representative statistics for each hydrologic variable. Thus, SELDM is an
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approach facilitates rapid specification of model parameters to develop planning-level estimates with available data. The approach allows for parsimony in the required inputs to and outputs from the model and flexibility in the use of the model. For example, SELDM can be used to model runoff from various land covers or land uses by using the highway-site definition as long as representative water quality and impervious-fraction data are available.
76:(TMDLs) for the site of interest and the upstream lake basin. The TMDL can be based on the average of annual loads because product of the average load times the number of years of record will be the sum-total load for that (simulated) period of record. The variability in annual values can be used to estimate the risk of exceedance and the margin of safety for the TMDL analysis 743: 118:
provides the calculated values for these variables. These statistics are different from the statistics commonly used to characterize or compare BMPs. They are designed to provide a stochastic transfer function to approximate the quantity, duration, and quality of BMP effluent given the associated inflow values for a population of storm events.
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performance of mitigation measures to produce a stochastic population of runoff-quality variables. Although SELDM is, nominally, a highway runoff model is can be used to estimate flows concentrations and loads of runoff-quality constituents from other land use areas as well. SELDM was developed by the
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mass-balance model. A mass-balance approach (figure 1) is commonly applied to estimate the concentrations and loads of water-quality constituents in receiving waters downstream of an urban or highway-runoff outfall. In a mass-balance model, the loads from the upstream basin and runoff source area are
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SELDM models the potential effect of mitigation measures by using Monte Carlo methods with statistics that approximate the net effects of structural and nonstructural best management practices (BMPs).. Structural BMPs are defined as the components of the drainage pathway between the source of runoff
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Jeznach, L. C., Granato, G. E., Sharar-Salgado, D., Jones, S. C., and Imig, D., 2023, Assessing potential effects of climate Change on highway-runoff flows and loads in southern New England by using planning-level space-for-time analyses: Transportation Research Record, v. 2677, no. 7, p. 570โ€“581,
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SELDM can do a stream-basin analysis and a lake-basin analysis. The stream-basin analysis uses a stochastic mass-balance analysis based on multi-year simulations including hundreds to thousands of runoff events. SELDM generates storm-event values for the site of interest (the highway site) and the
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Granato, G.E., Spaetzel, A.B., and Jeznach, L.C., 2023, Approaches for assessing flows, concentrations, and loads of highway and urban runoff and receiving-stream stormwater in southern New England with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey Scientific
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Granato, G.E., and Jones, S.C., 2015, Estimating the risks for adverse effects of total phosphorus in receiving streams with the Stochastic Empirical Loading and Dilution Model (SELDM) in Proceedings of the 2015 International Conference on Ecology and Transportation (ICOET 2015), September 20โ€“24,
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because the highway site, the upstream basin, and the lake basin each are represented as a single homogeneous unit. Each of these source areas is represented by average basin properties, and results from SELDM are calculated as point estimates for the site of interest. Use of the lumped parameter
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Granato, G.E., Spaetzel, A.B., and Jeznach, L.C., 2022, Model archive for analysis of flows, concentrations, and loads of highway and urban runoff and receiving-stream stormwater in southern New England with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey data
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Stonewall, A.J., Granato, G.E., and Glover-Cutter, K.M., 2019, Assessing potential effects of highway and urban runoff on receiving streams in total maximum daily load watersheds in Oregon using the Stochastic Empirical Loading and Dilution Model: U.S. Geological Survey Scientific Investigations
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quality model. SELDM is designed to transform complex scientific data into meaningful information about the risk of adverse effects of runoff on receiving waters, the potential need for mitigation measures, and the potential effectiveness of such management measures for reducing these risks. The
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used to calculate upstream and lake-basin transport curves was discovered and version 1.0.1 was released in July 2013. Version 1.0.2 was released in June, 2016 to use the Cunnane plotting position formula for all output files. Version 1.0.3 was released in July, 2018 to address issues with load
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The benefit of the Monte Carlo analysis is not to decrease uncertainty in the input statistics, but to represent the different combinations of the variables that determine potential risks of water-quality excursions. SELDM provides a method for rapid assessment of information that is otherwise
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with the associated highway-runoff variables. This report describes methods for calculating the trapezoidal-distribution statistics and rank correlation coefficients for stochastic modeling of volume reduction, hydrograph extension, and water-quality treatment by structural stormwater BMPs and
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SELDM is easy to use because it has a simple graphical user interface and because much of the information and data needed to run SELDM are embedded in the model. SELDM provides input statistics for precipitation, prestorm flow, runoff coefficients, and concentrations of selected water-quality
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The SELDM user interface has one or more GUI forms that are used to enter four categories of input data, which include documentation, site and region information, hydrologic statistics, and water-quality data. The documentation data include information about the analyst, the project, and the
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to help develop planning-level estimates of event mean concentrations, flows, and loads in stormwater from a site of interest and from an upstream basin. SELDM uses information about a highway site, the associated receiving-water basin, precipitation events, stormflow, water quality, and the
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The results of each SELDM analysis are written to 5โ€“10 output files, depending on the options that were selected during the analysis-specification process. The five output files that are created for every model run are the output documentation, highway-runoff quality, annual highway runoff,
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Granato, G.E., Spaetzel, A.B., and Medalie, L., 2021, Statistical methods for simulating structural stormwater runoff best management practices (BMPs) with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey Scientific Investigations Report 2020โ€“5136, 41 p.,
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Granato, G.E., Carlson, C.S., and Sniderman, B.S., 2009, Methods for development of planning-level stream-water-quality estimates at unmonitored sites in the conterminous United States: Washington, D.C., U.S. Department of Transportation, Federal Highway Administration, FHWA-HEP-09-003, 53
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so the model, source code, and all related documentation are provided free of any copyright restrictions according to U.S. copyright laws and the USGS Software User Rights Notice. SELDM is widely used to assess the potential effect of runoff from highways, bridges, and developed areas on
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Granato, G.E., and Friesz, P.J., 2021, Approaches for assessing long-term annual yields of highway and urban runoff in selected areas of California with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey Scientific Investigations Report 2021โ€“5043, 37 p.,
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to produce the random combinations of input variable values needed to generate the stochastic population of values for each component variable. SELDM calculates the dilution of runoff in the receiving waters and the resulting downstream event mean concentrations and annual average lake
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Granato, G.E., and Cazenas, P.A., 2009, Highway-Runoff Database (HRDB Version 1.0)--A data warehouse and preprocessor for the stochastic empirical loading and dilution model: Washington, D.C., U.S. Department of Transportation, Federal Highway Administration, FHWA-HEP-09-004, 57
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Weaver, J.C., Granato, G.E., and Fitzgerald, S.A., 2019, Assessing water quality from highway runoff at selected sites in North Carolina with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey Scientific Investigations Report 2019โ€“5031, 99 p.,
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under predevelopment and current conditions with the Stochastic Empirical Loading and Dilution Model (SELDM): in Proceedings of the 2017 World Environmental & Water Resources Congress, Sacramento, CA, May 21โ€“25, 2017, Reston, VA, American Society of Civil Engineers, 15 p.
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Risley, J.C., and Granato, G.E., 2014, Assessing potential effects of highway runoff on receiving-water quality at selected sites in Oregon with the Stochastic Empirical Loading and Dilution Model (SELDM): U.S. Geological Survey Scientific Investigations Report 2014โ€“5099, 74
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Granato, G.E., 2014, Statistics for stochastic modeling of volume reduction, hydrograph extension, and water-quality treatment by structural stormwater runoff best management practices (BMPs): U.S. Geological Survey Scientific Investigations Report 2014โ€“5037, 37 p.,
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receiving-water quality with and without the use of mitigation measures. Stormwater practitioners evaluating highway runoff commonly use data from the Highway Runoff Database (HRDB) with SELDM to assess the risks for adverse effects of runoff on receiving waters.
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Granato, G.E., and Jones, S.C., 2019, Simulating runoff quality with the Highway-Runoff Database and the Stochastic Empirical Loading and Dilution Model: Transportation Research Record, Journal of the Transportation Research Board, v. 2673, no. 1, p. 136-142,
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Stonewall, A.J., Granato, G.E., and Haluska, T.L., 2018, Assessing roadway contributions to stormwater flows, concentrations and loads by using the StreamStats application: Transportation Research Record, Journal of the Transportation Research Board, 9 p.
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Granato, G.E., 2010, Methods for development of planning-level estimates of stormflow at unmonitored sites in the conterminous United States: Washington, D.C., U.S. Department of Transportation, Federal Highway Administration, FHWA-HEP-09-005, 90
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In 2019, the USGS developed a model post processor for SELDM to facilitate analysis and graphing of results from SELDM simulations; that software, known as InterpretSELDM, is available in the public domain on a USGS ScienceBase site.
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Granato, G.E., and Jones, S.C., 2017, Estimating Total Maximum Daily Loads with the Stochastic Empirical Loading and Dilution Model: Transportation Research Record, Journal of the Transportation Research Board, No. 2638, p. 104-112.
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Figure 1. Schematic diagram showing the stochastic mass-balance approach for estimating stormflow, concentration, and loads of water-quality constituents upstream of a highway-runoff outfall, from the highway, and downstream of the
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National Academies of Sciences, Engineering, and Medicine, 2019, Approaches for Determining and Complying with TMDL Requirements Related to Roadway Stormwater Runoff. Washington, DC, The National Academies Press, 150 p.
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Stonewall, A.J., Yates, M.C., and Granato, G.E., 2022, Assessing the impact of chloride deicer application in the Siskiyou Pass, southern Oregon: U.S. Geological Survey Scientific Investigations Report 2022โ€“5091, 94 p.,
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Smith, K.P., Sorenson, J.R., and Granato, G.E., 2018, Characterization of stormwater runoff from bridge decks in eastern Massachusetts, 2014โ€“16: U.S. Geological Survey Scientific Investigations Report 2018โ€“5033, 73 p.,
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Helsel, D.R., and Hirsch, R.M., 2002, Statistical methods in water resourcesโ€”Hydrologic analysis and interpretation: U.S. Geological Survey Techniques of Water-Resources Investigations, book 4, chap. A3, 510
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Granato, G.E., 2012, Estimating basin lagtime and hydrograph-timing indexes used to characterize stormflows for runoff-quality analysis: U.S. Geological Survey Scientific Investigations Report 2012โ€“5110, 47
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Jeznach, L.C., and Granato, G.E., 2020, Comparison of SELDM simulated total-phosphorus concentrations with ecological impervious-area criteria: Journal of Environmental Engineering: v. 146, No. 8, 10 p.
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Smith, K.P., and Granato, G.E., 2010, Quality of stormwater runoff discharged from Massachusetts highways, 2005โ€“07: U.S. Geological Survey Scientific Investigations Report 2009โ€“5269, 198 p.
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Granato, G.E., 2019, InterpretSELDM version 1.0 The Stochastic Empirical Loading and Dilution Model (SELDM) output interpreter: U.S. Geological Survey software release,
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Stricker, V.A., and Sauer, V.B., 1982, Techniques for estimating flood hydrographs for ungaged urban watersheds: U.S. Geological Survey Open-File Report 82โ€“365, 24 p.
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Kacker, R.N., and Lawrence, J.F., 2007, Trapezoidal and triangular distributions for Type B evaluation of standard uncertainty: Metrologia, v. 44, no. 2, p. 117โ€“127.
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Granato, G.E., 2013, Stochastic empirical loading and dilution model (SELDM) version 1.0.0: U.S. Geological Survey Techniques and Methods, book 4, chap. C3, 112 p.
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Schwartz, S.S., and Naiman, D.Q., 1999, Bias and variance of planning-level estimates of pollutant loads: Water Resources Research, v. 35, no. 11, p. 3475โ€“3487.
138:ยฎ (VBA) interface controls to facilitate entry, processing, and output of data. Appendix 4 of the SELDM manual has detailed instructions for using the GUI. 166:(RDB) format that can be imported into many software packages. This output is designed to facilitate post-modeling analysis and presentation of results. 346:
Granato, G.E., 2022, Stochastic Empirical Loading and Dilution Model (SELDM) software archive (version 1.1.1): U.S. Geological Survey software release,
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Granato, G.E., 2022, Stochastic Empirical Loading and Dilution Model (SELDM) software archive: U.S. Geological Survey software release,
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Di Toro, D.M., 1984, Probability model of stream quality due to runoff: Journal of Environmental Engineering, v. 110, no. 3, p. 607โ€“628.
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Granato, G.E., 2014, SELDM: Stochastic Empirical Loading and Dilution Model version 1.0.3 Software support page available at
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Granato, G.E., and Jones, S.C., 2017, Estimating risks for water-quality exceedances of total-copper from highway and
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SELDM was developed between 2010 and 2013 and was published as version 1.0.0 in March 2013. A small problem with the
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added to calculate the discharge, concentration, and load in the receiving water downstream of the discharge point.
813: 130:ยฎ database software application to facilitate storage, handling, and use of the hydrologic dataset with a simple 131: 110: 73: 400:
2015, Raleigh, North Carolina: Raleigh, North Carolina, Center for Transportation and the Environment, 18 p.
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The annual flows and loads SELDM calculates for the stream and lake analyses also can be used to estimate
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Granato, G.E., 2019, Highway-Runoff Database (HRDB) Version 1.1.0: U.S. Geological Survey data release,
228: 163: 85: 240: 200: 249: โ€“ Science of the movement, distribution, and quality of water on Earth and other planets 204: 127: 114: 778: 375: 276: 264: 234: 93:
model based on data and statistics rather than theoretical physicochemical equations.
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Warn, A.E., and Brew, J.S., 1980, Mass balance: Water Research, v. 14, p. 1427โ€“1434.
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analysis. The site and region data include the highway-site characteristics, the
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code that can be downloaded from the SELDM software support page.
159: 58: 590: 208: 273: โ€“ Sub-field of hydrology concerned with above-earth water 134:(GUI). The program's menu-driven GUI uses standard Microsoft 237: โ€“ Land area where water converges to a common outlet 376:
http://ascelibrary.org/doi/abs/10.1061/9780784480601.028
439:https://doi.org/10.1061/(ASCE)EE.1943-7870.0001763 478: 476: 474: 472: 243: โ€“ Probabilistic problem-solving algorithm 23:stochastic empirical loading and dilution model 829:Water resource management in the United States 318: 316: 314: 312: 310: 308: 306: 304: 8: 285: โ€“ Assessment against standards for use 84:SELDM is a stochastic model because it uses 524:https://doi.org/10.1177/03611981231155183 483:Investigations Report 2023โ€“5087, 152 p., 578:https://doi.org/10.1177/0361198118758679 499:https://doi.org/10.1177/0361198118822821 38:developed SELDM in cooperation with the 300: 675:http://dx.doi.org/10.3133/sir20145037 279: โ€“ Contamination of water bodies 7: 689:https://doi.org/10.3133/sir20205136 604:https://doi.org/10.3133/sir20215043 485:https://doi.org/10.3133/sir20235087 452:https://doi.org/10.3133/sir20225091 426:https://doi.org/10.3133/sir20195031 412:https://doi.org/10.3133/sir20195053 389:https://doi.org/10.3133/sir20185033 255: โ€“ Randomly determined process 193:Per- and polyfluoroalkyl substances 750:from websites or documents of the 14: 746: This article incorporates 741: 734:https://doi.org/10.5066/P9PYG7T5 721:https://doi.org/10.5066/P9395YHY 511:https://doi.org/10.5066/P94VL32J 465:https://doi.org/10.5066/P9CZNIH5 348:https://doi.org/10.5066/P9PYG7T5 336:https://doi.org/10.5066/F7TT4P3G 834:United States Geological Survey 809:Environmental issues with water 752:United States Geological Survey 565:https://doi.org/10.3141/2638-12 324:http://pubs.usgs.gov/tm/04/c03/ 799:Federal Highway Administration 591:https://doi.org/10.17226/25473 40:Federal Highway Administration 1: 136:Visual Basic for Applications 819:Hydrology and urban planning 197:Perfluorooctanesulfonic acid 769:SELDM Software Support Page 199:), and tire chemicals (see 850: 410:Report 2019โ€“5053, 116 p., 824:Water and the environment 794:Environmental engineering 211:). The code for SELDM is 126:SELDM was developed as a 74:total maximum daily loads 764:SELDM Documentation Page 132:graphical user interface 111:trapezoidal distribution 16:Stormwater quality model 779:Stormwater YouTube Page 289:Water quality modelling 271:Surface-water hydrology 774:SELDM Software Archive 748:public domain material 98:lumped parameter model 65: 45:U.S. Geological Survey 36:U.S. Geological Survey 804:Stormwater management 62: 229:Computer simulation 164:relational database 86:Monte Carlo methods 241:Monte Carlo method 201:Tire manufacturing 66: 191:, PFAS/PFOS (see 80:Model description 841: 814:Hydrology models 745: 744: 736: 730: 724: 717: 711: 707: 701: 698: 692: 684: 678: 670: 664: 661: 655: 651: 645: 642: 636: 632: 626: 622: 616: 612: 606: 599: 593: 586: 580: 573: 567: 560: 554: 551: 545: 542: 536: 533: 527: 519: 513: 507: 501: 494: 488: 480: 467: 460: 454: 447: 441: 434: 428: 421: 415: 407: 401: 397: 391: 384: 378: 367: 361: 357: 351: 344: 338: 332: 326: 320: 205:Rubber pollution 162:text files in a 128:Microsoft Access 115:rank correlation 849: 848: 844: 843: 842: 840: 839: 838: 784: 783: 760: 742: 739: 731: 727: 718: 714: 708: 704: 699: 695: 685: 681: 671: 667: 662: 658: 652: 648: 643: 639: 633: 629: 623: 619: 613: 609: 600: 596: 587: 583: 574: 570: 561: 557: 552: 548: 543: 539: 534: 530: 520: 516: 508: 504: 495: 491: 481: 470: 461: 457: 448: 444: 435: 431: 422: 418: 408: 404: 398: 394: 385: 381: 368: 364: 358: 354: 345: 341: 333: 329: 321: 302: 298: 277:Water pollution 225: 180: 152: 124: 122:Model interface 82: 17: 12: 11: 5: 847: 845: 837: 836: 831: 826: 821: 816: 811: 806: 801: 796: 786: 785: 782: 781: 776: 771: 766: 759: 758:External links 756: 738: 737: 725: 712: 702: 693: 679: 665: 656: 646: 637: 627: 617: 607: 594: 581: 568: 555: 546: 537: 528: 514: 502: 489: 468: 455: 442: 429: 416: 402: 392: 379: 362: 352: 339: 327: 299: 297: 294: 293: 292: 286: 280: 274: 268: 265:Surface runoff 262: 256: 250: 244: 238: 235:Drainage basin 232: 224: 221: 179: 176: 151: 148: 123: 120: 81: 78: 15: 13: 10: 9: 6: 4: 3: 2: 846: 835: 832: 830: 827: 825: 822: 820: 817: 815: 812: 810: 807: 805: 802: 800: 797: 795: 792: 791: 789: 780: 777: 775: 772: 770: 767: 765: 762: 761: 757: 755: 753: 749: 735: 729: 726: 722: 716: 713: 706: 703: 697: 694: 690: 683: 680: 676: 669: 666: 660: 657: 650: 647: 641: 638: 631: 628: 621: 618: 611: 608: 605: 598: 595: 592: 585: 582: 579: 572: 569: 566: 559: 556: 550: 547: 541: 538: 532: 529: 525: 518: 515: 512: 506: 503: 500: 493: 490: 486: 479: 477: 475: 473: 469: 466: 459: 456: 453: 446: 443: 440: 433: 430: 427: 420: 417: 413: 406: 403: 396: 393: 390: 383: 380: 377: 372: 366: 363: 356: 353: 349: 343: 340: 337: 331: 328: 325: 319: 317: 315: 313: 311: 309: 307: 305: 301: 295: 290: 287: 284: 283:Water quality 281: 278: 275: 272: 269: 266: 263: 260: 257: 254: 251: 248: 245: 242: 239: 236: 233: 230: 227: 226: 222: 220: 218: 217:public domain 214: 210: 206: 202: 198: 194: 190: 189:Microplastics 185: 177: 175: 171: 167: 165: 161: 158: 157:tab-delimited 149: 147: 145: 139: 137: 133: 129: 121: 119: 116: 112: 106: 102: 99: 94: 92: 87: 79: 77: 75: 70: 61: 57: 54: 49: 46: 41: 37: 32: 28: 24: 19: 740: 728: 715: 705: 696: 682: 668: 659: 649: 640: 630: 620: 610: 597: 584: 571: 558: 549: 540: 531: 517: 505: 492: 458: 445: 432: 419: 405: 395: 382: 371:urban runoff 365: 355: 342: 330: 181: 172: 168: 153: 150:Model output 140: 125: 107: 103: 95: 83: 71: 67: 50: 26: 22: 20: 18: 213:open source 96:SELDM is a 51:SELDM is a 788:Categories 296:References 259:Stormwater 253:Stochastic 144:ecoregions 53:stochastic 31:stormwater 463:release, 247:Hydrology 184:algorithm 91:empirical 223:See also 113:and the 178:History 64:outfall 29:) is a 207:, and 160:ASCII 27:SELDM 215:and 209:6PPD 195:and 21:The 790:: 754:. 710:p. 654:p. 635:p. 625:p. 615:p. 471:^ 360:p. 303:^ 203:, 723:. 691:. 677:. 526:. 487:. 414:. 350:. 25:(

Index

stormwater
U.S. Geological Survey
Federal Highway Administration
U.S. Geological Survey
stochastic

total maximum daily loads
Monte Carlo methods
empirical
lumped parameter model
trapezoidal distribution
rank correlation
Microsoft Access
graphical user interface
Visual Basic for Applications
ecoregions
tab-delimited
ASCII
relational database
algorithm
Microplastics
Per- and polyfluoroalkyl substances
Perfluorooctanesulfonic acid
Tire manufacturing
Rubber pollution
6PPD
open source
public domain
Computer simulation
Drainage basin

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