HRU
160
Highest simulated upland sediment-yield HRU in the present model assessment.
Hydrologic Response Units (HRUs) were developed for the Hare River watershed by combining land use, soil and terrain-slope information. The HRU framework enables SWAT to represent spatial variations in runoff generation, infiltration, evapotranspiration, soil-water storage, subsurface flow and erosion within each modelled subbasin.
Following completion of watershed delineation, the land-use, soil and slope datasets were reclassified into SWAT-compatible classes and overlaid. The final HRU definition retained all valid combinations of land use, soil and slope by applying zero-percent elimination thresholds.
The completed HRU framework has now been used successfully in continuous SWAT simulations for the approximately 161.95 km² Hare River watershed.
| Component | Dataset / Method | Status |
|---|---|---|
| Watershed delineation | DEM-derived ArcSWAT watershed | Completed |
| Watershed area | Approximately 161.95 km² | Completed |
| Subbasins | 17 hydrologically connected SWAT subbasins | Completed |
| Land use | HARE 2026 land-use / land-cover reconstruction | Completed |
| Soils | HARE watershed soil raster | Completed |
| Slope | DEM-derived five-class slope system | Completed |
| Land-use / soil / slope overlay | ArcSWAT Full HRU overlay | Completed |
| HRU definition | Multiple HRUs with 0% elimination thresholds | Completed |
| Weather preparation | NASA POWER daily meteorological forcing, 2020–2025 | Completed |
| Weather generator | Hare-specific weather-generator setup prepared and tested | Completed |
| SWAT database tables | Required model input tables generated successfully | Completed |
| Continuous SWAT simulation | Two successful daily simulations, 2020–2025 | Completed |
| HRU response assessment | Runoff, water balance and sediment response | In progress |
The land-use raster was clipped to the Hare River watershed and reclassified into SWAT land-use categories. Six principal land-use classes were retained within the final watershed.
| Original Class | SWAT Code | Watershed Share | SWAT Representation |
|---|---|---|---|
| Trees | FRST | 34.42% | Forest |
| Cropland | AGRL | 26.17% | Agricultural land |
| Grass | RNGE | 20.73% | Range grasses |
| Shrub / Scrub | RNGB | 11.71% | Range brush |
| Built-up | URMD | 6.61% | Urban medium density |
| Bare ground | BARR | 0.36% | Barren land |
Trees represent the largest mapped land-use component of the watershed, followed by cropland and grassland. Retaining these classes separately allows SWAT to apply different vegetation, interception, evapotranspiration, infiltration, runoff and erosion characteristics.
The original soil raster covered an area larger than the final Hare watershed. It was therefore clipped to the SWAT watershed boundary before soil classification and HRU generation.
Within the final watershed boundary, the retained mapped soil unit was:
| Mapped Soil Code | SWAT User Soil | Watershed Representation |
|---|---|---|
| 257 | To6-2bc-257 | 100% of the final SWAT watershed soil layer |
The soil assignment provides SWAT with the soil-profile characteristics required for calculation of infiltration, soil-water storage, percolation, lateral flow, groundwater recharge and erosion processes.
Terrain slope was calculated directly from the same digital elevation model used for watershed delineation. A five-class slope system was adopted so that differences between relatively gentle terrain and the steep upper watershed could be represented explicitly within the HRUs.
| Slope Class | Slope Range | General Terrain Interpretation |
|---|---|---|
| 1 | 0–5% | Gentle terrain |
| 2 | 5–15% | Gentle to moderate slopes |
| 3 | 15–30% | Moderately steep terrain |
| 4 | 30–60% | Steep terrain |
| 5 | >60% | Very steep terrain |
Slope is particularly important in the Hare watershed because it influences surface-runoff velocity, erosion potential, infiltration opportunity and the rate at which water and sediment are transferred from the upper watershed toward the drainage network.
After the three spatial datasets had been successfully reclassified, ArcSWAT performed a Full HRU overlay. Each resulting Hydrologic Response Unit represents a unique combination of land use, soil and slope within a particular subbasin.
Conceptually, the HRU generation can be represented as:
Subbasin + Land Use + Soil + Slope → Hydrologic Response Unit
For example, cropland occurring on soil unit 257 within a 5–15% slope band is treated differently from forest occurring on the same mapped soil unit but on a slope exceeding 60%.
This allows SWAT to preserve hydrological differences associated with vegetation, land management, soil properties and terrain while routing runoff, subsurface flow and sediment through the subbasin and stream network.
The Multiple HRUs option was used for the final HRU definition. Percentage-based thresholds were selected and all three elimination thresholds were set to zero.
| HRU Criterion | Threshold | Effect |
|---|---|---|
| Land use | 0% | All valid land-use classes retained |
| Soil | 0% | All valid soil combinations retained |
| Slope | 0% | All valid slope classes retained |
The zero-percent thresholds were intentionally adopted so that small but potentially important land-use or terrain combinations would not be eliminated automatically.
This decision has proved useful during interpretation of the completed SWAT simulations because a very small bare-ground area emerged as one of the most important simulated erosion sources.
The completed SWAT simulations demonstrate why retaining the full HRU structure was important. Different land-cover and terrain combinations produce markedly different runoff and sediment responses.
The strongest simulated erosion response occurs within the BARR — bare-ground land-use class. Although this class occupies only about 0.58 km², or approximately 0.36% of the watershed, its simulated runoff and erosion are substantially greater than the watershed average.
| Indicator | Bare-Ground Response | Interpretation |
|---|---|---|
| SWAT land-use code | BARR | Barren / exposed land |
| Approximate area | 0.58 km² | Small fraction of total watershed |
| Watershed share | 0.36% | Highly localized land-cover class |
| Curve Number | 91 | High runoff potential |
| Surface runoff | 663.81 mm | Very strong simulated runoff response |
| Average sediment yield | 1,549.33 Mg/ha | Extremely high localized erosion response |
In sediment terminology:
1 Mg = 1 metric tonne = 1,000 kg
The basin-wide average upland sediment yield from Simulation 2 was much lower, at approximately 58.4 Mg/ha, while the SWAT sediment assessment also indicated substantial deposition within the channel system.
The SWAT Error Checker identified a localized HRU with an exceptionally high simulated erosion rate.
160
Highest simulated upland sediment-yield HRU in the present model assessment.
6
The erosion hotspot is located within SWAT Subbasin 6.
BARR
Bare or exposed ground forms the critical land-cover condition.
The identification of this hotspot provides a useful target for future spatial review. The corresponding location can be examined against satellite imagery, terrain slope and field conditions to determine whether the simulated erosion is physically representative.
HEC-HMS and SWAT are used for different but complementary hydrological purposes in the HARE Irrigation Project reassessment.
| Model | Primary Role in the HARE Study |
|---|---|
| HEC-HMS | Event-based rainfall-runoff modelling, design-flood estimation and flood-hydrograph development for the Hare diversion weir. |
| SWAT | Continuous watershed simulation including runoff, evapotranspiration, soil-water processes, groundwater contribution, streamflow, erosion, sediment transport and channel deposition. |
The HRU framework is fundamental to the SWAT analysis because it provides the spatial units through which rainfall is transformed into evapotranspiration, infiltration, soil-water storage, surface runoff, lateral flow and groundwater recharge before water reaches the stream network.
HRUs also provide the spatial basis for estimating soil erosion. Consequently, a small area with exposed soil and steep terrain can contribute disproportionately to sediment production even when that land-cover class occupies only a small fraction of the total watershed.
The HRU analysis provides the source-area component of the sediment assessment, while SWAT channel routing describes how that material may be transported and deposited within the river system.
Simulation 2 produced an average upland sediment yield of approximately 58.4 Mg/ha and indicated strong net sediment deposition within the stream network.
Present-day field photographs and video of the Hare diversion weir show substantial accumulations of gravel, sand and finer sediment both upstream and downstream of the structure.
The field observations do not constitute formal numerical calibration of the SWAT sediment model. Nevertheless, the observed condition of the river provides an important physical consistency check on the modelled finding that sediment production and deposition are significant processes within the Hare watershed.
HRU generation is no longer a preparatory stage of the Hare SWAT model. The HRU framework has now been successfully used in two continuous watershed simulations.
Complete
Watershed, subbasins, land use, soil, slope and HRUs are established.
Complete
Daily NASA POWER climate forcing for 2020–2025 has been incorporated successfully.
2 Runs
Two continuous SWAT simulations have completed successfully with similar overall watershed behaviour.
View SWAT watershed delineation | View SWAT climate-input preparation