Indicator Reference Sheet - March 6, 2022

Soil Runoff Potential

U.S. Environmental Protection Agency

Indicator Names

•	% Low Runoff Potential Soils in Watershed (WS)

•	% Moderately Low Runoff Potential Soils in Watershed (WS)
% Moderately High Runoff Potential Soils in Watershed (WSj
% High Runoff Potential Soils in Watershed (WS)

Indicator Description
Background

Soil runoff potential describes the likelihood for surface
runoff to occur during rainfall or snowmelt. Surface runoff
is generated when the movement of water into the soil is
slow enough to result in water flow along the land surface
and into waterbodies.

Soil scientists have defined and mapped four categories of
soil runoff potential, termed Hydrologic Soil Groups1 The
classification of soils into Hydrologic Soil Groups is based
on characteristics such as soil texture and degree of
compaction, or by measured rates of downward water
movement in the soil.1 The water table depth and the
depth to an impermeable layer are also considered.1

What the Indicators Measure

These indicators measure the area of each Hydrologic Soil
Group in a HUC12 subwatershed:*

•	% Low Runoff Potential Soils in Watershed (WS) -
area of soils in Hydrologic Soil Group A (low runoff
potential) in the HUC12 (Figure 1). Expressed as a
percentage of the total HUC12 area.

•	% Moderately Low Runoff Potential Soils in WS - a re a
of soils in Hydrologic Soil Group B (moderately low
runoff potential) in the HUC12. Expressed as a
percentage of the total HUC12 area

•	% Moderately High Runoff Potential Soils in WS -
area of soils in Hydrologic Soil Group C (moderately
high runoff potential) in the HUC12. Expressed as a
percentage of the total HUC12 area.

•	% High Runoff Potential Soils in WS - area of soils in
Hydrologic Soil Group D (high runoff potential) in the
HUC12. Expressed as a percentage of the total HUC12
area.

The indicators of low and moderately low runoff potential
are classified as Ecological indicators. The indicators of
high and moderately high runoff potential are classified as
Stressor Indicators.

Relevance to Water Quality Restoration and Protection
Soil runoff potential plays a fundamental role in the
hydrology of a watershed and its water quality.2 Soil runoff

Indicator Category | Ecological and Stressor

I

Subcategory | Soil Attributes
Available in RPS Tool files for all lower 48 states

o%

>45%

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Mapped.

Figure 1. Map of % Low Runoff Potential Soils in Watershed

for HUC12s across the contiguous US.

potential, along with topography and land use, largely
determine the relative amount of precipitation that drains
across the surface versus percolates into groundwater.2-3
Understanding a watershed's hydrology is key to
diagnosing potential sources of pollution.4,5

Soils with high runoff potential, such as soils with high clay
content, can amplify issues related to nonpoint source
pollution because runoff may flush sediment, nutrients,
pathogens, and other pollutants from the landscape and
into nearby waters.2-4 In contrast, soils with low runoff
potential, like sandy soils, can better allow precipitation to
filter through the soil and recharge groundwater
supplies.2,4 Note, however, that certain pollutants which
readily dissolve in water, such as nitrate, can still pose
issues in areas with low runoff potential because the
pollutants can leach into groundwater and become a long-
term pollutant source to surface waters.5

Soil runoff potential has been used by the US Department
of Agriculture (USDA) Natural Resources Conservation
Service (NRCS) to estimate the vulnerability of soils to
sediment, phosphorus, and nitrogen loss and to quantify
the benefits of land conservation practices.7 The US Forest
Service has also included soil runoff potential as an
indicator of the vulnerability of watersheds to climate
change.8 In this vulnerability assessment, soil runoff
potential was factored in an evaluation of future changes

* HUC12s are subwatershed delineations in the National

Watershed Boundary Dataset. HUC12s are referenced by
their 12-digit Hydrologic Unit Code.


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in erosion and groundwater recharge that may occur on
forested lands.8

These indicators can be used to identify HUC12s that are
dominated by soils with high runoff potential and to assess
the vulnerability of HUC12s to future degradation due to
more frequent and intense rainfall or other types of
climate change. Additional indicators, such as land use
trends, can also be included in an evaluation of watershed
vulnerability to gain a more complete picture of potential
climate change impacts on watersheds.

Processing Method

These indicators are measured from soil data in the
Natural Resources Conservation Service (NRCS) Gridded
Soil Survey Geographic Database (gSSURGO). The
gSSURGO database maps the location of soil types across
the nation at a resolution of 10 meters or approximately
33 feet. The July 2020 version of gSSURGO was used for
analysis of the soil runoff potential indicators.

The gSSURGO database reports numeric and descriptive
attributes of each soil type in the database, including the
Hydrologic Soil Group assigned to soil types based on field
surveys completed by soil scientists.

Hydrologic Soil Group

HA - Low Runoff Potential

¦	B - Moderately Low Runoff Potential
SC - Moderately High Runoff Potential

¦	D - High Runoff Potential

Figure 2. Example map of Hydrologic Soil Group classifications
in a HUC12 subwatershed.

To calculate the percentage of a HUC12 covered by each
Hydrologic Soil Group, a map layer of the dominant
Hydrologic Soil Group per soil type was created from the
gSSURGO database and was overlaid with IHUC12
boundaries (Figure 2). The area of each Hydrologic Soil
Group was then calculated per HUC12 and converted to a
percentage of total HUC12 area.

Limitations

• Hydrologic Soil Group is not reported for every soil type
in the gSSURGO database. A missing area threshold of

50% was used for reporting values of the soil runoff
potential indicators. Blank values are reported for
HUC12s that are missing Hydrologic Soil Group in 50%
or more of the HUC12 area.

•	The slope of the soil surface and land cover are not
considered when assigning Hydrologic Soil Groups.1

•	The classification of soils into Hydrologic Soil Groups is
based on the judgment of soil scientists, primarily
relying on their interpretation of criteria found in either
the NRCS National Engineering Handbook or National
Soil Survey Handbook. As a result, large-scale mapping
of hydrologic soil groups can be susceptible to
inconsistencies and inaccuracies.6 Efforts that require a
detailed analysis of soil conditions should consult soil
survey reports for the area of interest.

Links to Access Data and Additional Information
HUC12 indicator data can be accessed within the EPA
Restoration and Protection Screening (RPS) Tool, in
downloadable data files, or as a web service. Visit the EPA
RPS website for links to access the RPS Tool, HUC12
indicator database, and web service.

The gSSURGO dataset used to calculate these indicators is
accessible from the NRCS gSSURGO website.

References

^ockus, V., et al. 2009. Part 630 Hydrology National
Engineering Handbook, Chapter 7: Hydrologic soil
groups. Natural Resources Conservation Service.

2Allan, J., et al. 2020. Stream ecology: structure and
function of running waters. Springer Nature.

30'Geen, A., 2013. Soil Water Dynamics. Nature Education
Knowledge. 4(5): 9.

4Winter, T., et al. 1998. Ground water and surface water: a
single resource. US Geological Survey. Vol. 1139.

5Mueiler, D., et al. 1995. Nutrients in ground water and
surface water of the United States: An analysis of data
through 1992 US Geological Survey. 95: 4031

"Abraham, S., et al. 2020. Classification of soils into
hydrologic groups using machine learning. Data. 5(1): 2.

7USDA NRCS. 2012. Assessment of the Effects of
Conservation Practices on Cultivated Cropland in the
Upper Mississippi River Basin.

8US Forest Service. 2013. Assessing the Vulnerability of
Watersheds to Climate Change. General Technical Report
PNW-GTR-884.


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