Model:HSPF: Difference between revisions
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EPA has information about HSPF, but no longer has active support for HSPF as a standalone model. See also: https://www.epa.gov/ceam/hydrological-simulation-program-fortran-hspf | |||
{{Model identity | {{Model identity | ||
|Model type=Modular | |Model type=Modular | ||
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{{Model identity2 | {{Model identity2 | ||
|ModelDomain=Hydrology, Terrestrial | |||
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|Spatial dimensions=2D | |Spatial dimensions=2D | ||
|Spatialscale=Landscape-Scale, Watershed-Scale | |Spatialscale=Landscape-Scale, Watershed-Scale | ||
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|Town / City=Athens | |Town / City=Athens | ||
|Postal code=30605-2700 | |Postal code=30605-2700 | ||
|Country=United States | |||
|State=Georgia | |State=Georgia | ||
|Email address=test@test.com | |Email address=test@test.com | ||
|Phone=706-355-8403 | |Phone=706-355-8403 | ||
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|Code optimized=Single Processor | |Code optimized=Single Processor | ||
|Start year development=1997 | |Start year development=1997 | ||
|Program license type=Other | |Program license type=Other | ||
|Program license type other=-- | |Program license type other=-- | ||
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{{Model testing | {{Model testing | ||
|Describe available calibration data sets=SPF and the earlier models from which it was developed have been extensively | |Describe available calibration data sets=SPF and the earlier models from which it was developed have been extensively applied in a wide variety of hydrologic and water quality studies (3,4), including pesticide runoff model testing (5), aquatic fate and transport model testing (6,7), and analyses of agricultural best management practices (8,9). An application of HSPF in a screening methodology for pesticide review is described by Donigian et al. (10). In addition, HSPF has been validated with both field data and model experiments, and has been reviewed by independent experts (11-20). | ||
applied in a wide variety of hydrologic and water quality studies (3,4), | |||
including pesticide runoff model testing (5), aquatic fate and transport | |||
model testing (6,7), and analyses of agricultural best management practices | |||
(8,9). | |||
review is described by Donigian et al. (10). In addition, HSPF has been | |||
validated with both field data and model experiments, and has been reviewed | |||
by independent experts (11-20). | |||
The Stream Transport and Agricultural Runoff for Exposure Assessment | The Stream Transport and Agricultural Runoff for Exposure Assessment Methodology (STREAM) applies the HSPF program to various test watersheds for five major crops in four agricultural regions in the United States, defines a "representative" watershed based on regional conditions and an extrapolation of the calibration for the test watershed, and performs a sensitivity analysis on key pesticide parameters to generate cumulative frequency distributions of pesticide loads and concentrations in each regions. The resulting methodology requires the user to evaluate only the crops and regions of interest, the pesticide application rate, and three pesticide parameters -- the partition coefficient, the soil/sediment decay rate, and the solution decay rate. | ||
Methodology (STREAM) applies the HSPF program to various test watersheds for | |||
five major crops in four agricultural regions in the United States, | |||
defines a "representative" watershed based on regional conditions and an | |||
extrapolation of the calibration for the test watershed, and performs a | |||
sensitivity analysis on key pesticide parameters to generate cumulative | |||
frequency distributions of pesticide loads and concentrations in each | |||
regions. | |||
crops and regions of interest, the pesticide application rate, and three | |||
pesticide parameters -- the partition coefficient, the soil/sediment decay | |||
rate, and the solution decay rate. | |||
The EPA Chesapeake Bay Program has been using the HSPF model as the framework | The EPA Chesapeake Bay Program has been using the HSPF model as the framework for modeling total watershed contributions of flow, sediment, and nutrients (and associated constituents such as water temperature, DO, BOD, etc.) to the tidal region of the Chesapeake Bay (21,22). The watershed modeling represents pollutant contributions from an area of more than 68,000 sq. mi., and provides the input to drive a fully dynamic three-dimensional, hydrodynamic/water quality model of the Bay. The watershed drainage area is divided into land segments and stream channel segments. The land areas modeled include forest, agricultural cropland (conventional and conservation tillage systems), pasture, urban (pervious and impervious areas), and uncontrolled animal waste contributions. The stream channel simulation includes flow routing and oxygen and nutrient biochemical modeling (through phytoplankton) in order to account for instream processes affecting nutrient delivery to the Bay. | ||
for modeling total watershed contributions of flow, sediment, and nutrients | |||
(and associated constituents such as water temperature, DO, BOD, etc.) to the | |||
tidal region of the Chesapeake Bay (21,22). | |||
represents pollutant contributions from an area of more than 68,000 sq. mi., | |||
and provides the input to drive a fully dynamic three-dimensional, | |||
hydrodynamic/water quality model of the Bay. The watershed drainage area is | |||
divided into land segments and stream channel segments. The land areas | |||
modeled include forest, agricultural cropland (conventional and conservation | |||
tillage systems), pasture, urban (pervious and impervious areas), and | |||
uncontrolled animal waste contributions. The stream channel simulation | |||
includes flow routing and oxygen and nutrient biochemical modeling (through | |||
phytoplankton) in order to account for instream processes affecting nutrient | |||
delivery to the Bay. | |||
Currently, buildup/washoff type algorithms are being used for urban | Currently, buildup/washoff type algorithms are being used for urban impervious areas, potency factors for all pervious areas, and constant (or seasonally variable) concentrations for all subsurface contributions and animal waste components. Enhancements are underway to utilize the detailed process (i.e. Agrichemical modules) simulation for cropland areas to better represent the impacts of agricultural BMPs and to include nitrogen cycling in forested systems to evaluate the impacts of atmospheric deposition of nitrogen on Chesapeake Bay. The watershed modeling is being used to evaluate nutrient management alternatives for attaining a 40% reduction in nutrient loads delivered to the Bay, as defined in a joint agreement among the governors of the member states. | ||
impervious areas, potency factors for all pervious areas, and constant (or | |||
seasonally variable) concentrations for all subsurface contributions and | |||
animal waste components. Enhancements are underway to utilize the detailed | |||
process (i.e. Agrichemical modules) simulation for cropland areas to better | |||
represent the impacts of agricultural BMPs and to include nitrogen cycling in | |||
forested systems to evaluate the impacts of atmospheric deposition of | |||
nitrogen on Chesapeake Bay. The watershed modeling is being used to evaluate | |||
nutrient management alternatives for attaining a 40% reduction in nutrient | |||
loads delivered to the Bay, as defined in a joint agreement among the | |||
governors of the member states. | |||
}} | }} | ||
{{Users groups model | {{Users groups model | ||
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{{Documentation model | {{Documentation model | ||
|Manual model available=Yes | |Manual model available=Yes | ||
|Model website if any=http:// | |Model website if any=http://water.epa.gov/scitech/datait/models/basins/bsnsdocs.cfm#hspf The HSPF User's Manual is available as a WordPerfect (version 5.1) document in (binary, non-ASCII) files HSPF_V11.001, HSPF_V11.002, HSPF_V11.003, | ||
HSPF_V11.004, HSPF_V11.005, HSPF_V11.006, and HSPF_V11.007 in the DOCUMENT | HSPF_V11.004, HSPF_V11.005, HSPF_V11.006, and HSPF_V11.007 in the DOCUMENT | ||
sub-directory. Refer to file READ.ME in the README sub-directory for further | sub-directory. Refer to file READ.ME in the README sub-directory for further | ||
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{{CSDMS staff part | {{CSDMS staff part | ||
|OpenMI compliant=No but possible | |OpenMI compliant=No but possible | ||
|IRF interface=No but possible | |||
|CMT component=No but possible | |||
|CCA component=No but possible | |CCA component=No but possible | ||
}} | }} | ||
{{Start coupled table}} | {{Start coupled table}} | ||
{{End a table}} | {{End a table}} | ||
{{End headertab}} | {{End headertab}} | ||
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<!-- PLEASE USE THE "EDIT WITH FORM" BUTTON TO EDIT ABOVE CONTENTS; CONTINUE TO EDIT BELOW THIS LINE --> | <!-- PLEASE USE THE "EDIT WITH FORM" BUTTON TO EDIT ABOVE CONTENTS; CONTINUE TO EDIT BELOW THIS LINE --> | ||
==Introduction== | ==Introduction== | ||
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== History == | == History == | ||
== | == References == | ||
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== Issues == | == Issues == | ||
== Help == | == Help == | ||
{{#ifexist:Model_help:{{PAGENAME}}|[[Model_help:{{PAGENAME}}]]|}} | |||
== Input Files == | == Input Files == | ||
== Output Files == | == Output Files == | ||
Latest revision as of 20:14, 16 September 2020
EPA has information about HSPF, but no longer has active support for HSPF as a standalone model. See also: https://www.epa.gov/ceam/hydrological-simulation-program-fortran-hspf
HSPF
Metadata
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Introduction
History
References
Nr. of publications: | 351 |
Total citations: | 11177 |
h-index: | 48 |
m-quotient: | 1.12 |
Featured publication(s) | Year | Model described | Type of Reference | Citations |
---|---|---|---|---|
Bicknell, B.R.; Imhoff, J.C.; Kittle, J.L.; Donigian, A.S.; Johanson, R.C.; 1993. Hydrological Simulation Program - FORTRAN (HSPF): Users Manual for Release 10.. EPA-600/R-93/174, , . (View/edit entry) | 1993 | HSPF |
Model overview | 341 |
See more publications of HSPF |