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SWAT Baseline Model for Soldier Creek, KS, USA


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Created: May 27, 2025 at 3:39 p.m. (UTC)
Last updated: May 27, 2025 at 4:39 p.m. (UTC)
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Content types: Geographic Feature Content  Model Program Content  Model Instance Content 
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Abstract

Authors:
Naomi DetenbeckAlyssa Le
Owners: Naomi Detenbeck
Type: Resource
Storage: The size of this resource is 53.7 MB
Created: May 27, 2025 at 1:35 p.m.
Last updated: May 27, 2025 at 3:38 p.m.
Citation: See how to cite this resource
Content types: Single File Content Geographic Feature Content
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Abstract
We created a baseline SWAT model for 1995-2015 (including a 2-year warm-up period) at the HUC12-scale using the HAWQS v1 system. We used default data included with the HAWQS v1 system, including land-cover derived from NLCD 2006 and the Cropland Data Layer (2011-2012) and weather inputs from the HAWQS PRISM database. We updated the SWAT model to include point source inputs from wastewater effluent that were derived from (a) the EPA ECHO database (https://echo.epa.gov/trends/loading-tool/get-data/watershed-statistics) for TSS and (b) the Hypoxia Task Force database for TP (https://echo.epa.gov/trends/loading-tool/hypoxia-task-force-nutrient-model) We assumed 57% of TP effluent from wastewater is soluble reactive P, 2.8% is organic P and 40% is particulate mineral P (total of 97% mineral P and 3% organic P). For the Potawatomie treatment plant, modeled discharge values were used in place of measured values because violations had been reported due to inadequate flow calibrations at the facility. We also added initial groundwater concentrations of 0.1 mg N/L for NO3-N and 0.0433 mg P/L for soluble P to replace default SWAT values of zero.
The baseline SWAT model from HAWQS was modified to represent existing agricultural management activities. Information on existing agricultural conservation practices in the USC (cover crops, residue and tillage management, contouring, terraces, filter strips, controlled stream access for cattle, managed grazing), as of 2015 were compiled from KDHE (Andrew S. Lyon, KDHE, pers. comm.). To model the effects of cattle grazing and associated BMPs, we used methodology described in Sheshukov et al. (2016)]; See Supplemental Material 2)). Following guidance in Waidler et al. (2009), cover crops were implemented using the land use update (lup) table in SWAT and modifying HRU fraction (HRU_FRC) to simultaneously convert area from converted crop land (CORN or SOY or CORNSOY combinations) to SOYWW (soy/winter wheat) or WWSY (winter wheat/soy) sequences. The baseline SWAT model for USC, including existing BMPs (Contouring (736 acres treated), Grassed waterways (2965 acres), No till (966 acres), Terracing (966 acres), Vegetative filter strips (848 acres), Created agricultural wetlands (36 acres treated) and cattle grazing, was calibrated using the SUFI-2 (Sequential Uncertainty Fitting version 2 using SWAT-CUP.] This model set-up includes the swat670-WMOST version which formats output for use in US EPA's Watershed Management Optimization Support Tool.

Subject Keywords

Coverage

Spatial

Coordinate System/Geographic Projection:
WGS 84 EPSG:4326
Coordinate Units:
Decimal degrees
Place/Area Name:
Soldier Creek, Kansas
North Latitude
39.6578°
East Longitude
-95.8141°
South Latitude
39.2426°
West Longitude
-96.0260°

Temporal

Start Date:
End Date:

Content

Credits

Funding Agencies

This resource was created using funding from the following sources:
Agency Name Award Title Award Number
United States Environmental Protection Agency

How to Cite

Detenbeck, N., A. Le (2025). SWAT Baseline Model for Soldier Creek, KS, USA, HydroShare, http://www.hydroshare.org/resource/22e72bca6f754ac0a2ccc831ced21f22

This resource is shared under the Creative Commons Attribution CC BY.

http://creativecommons.org/licenses/by/4.0/
CC-BY

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