Assessing soil health and function

This site is currently undergoing revision. For more information, open this link.
Site is in development

Indicators for determining soil health
Indicator	Vegetative growth	Soil biotic function	Soil hydrologic function	Soil erosion potential
Compaction/bulk density	Yes	Yes	Yes	If surface compacted
Water stable aggregates	Yes
Soil nutrient status	Yes
Soil structure	Yes
Plant roots	Yes

Soil health is an assessment of how well soil performs all of its functions now and how those functions are being preserved for future use. The assessment of soil health depends on the desired functions of the soil. In agricultural applications, for example, soil health is determined by assessing properties that affect plant growth, such nutrient status, pH, and bulk density.

For stormwater applications, soil health can be assessed for the following functions.

• Ability to support vegetative growth
• Fully functioning soil ecology
• Supporting hydraulic/hydrologic function
• Ability to minimize erosion

Each of these is discussed below.

Ability to support vegetative growth

The following indicators can be used to assess suitability of a soil to support plant/vegetative growth.

Vegetative growth - Soil compaction (bulk density)

Curve showing relationship of root penetration and penetration resistance. Source: Penn State University Extension.

Importance: Soil compaction results from repeated traffic, generally from machinery, or repeated tillage at the same depth, which results in a compacted layer at the tillage depth. Compaction inhibits infiltration, gas and water movement, may impede root growth, disrupts habitat for soil biota, and affects nutrient cycling. See Soil physical properties and processes for a discussion of bulk density.

Assessment There are multiple methods for measuring bulk density and compaction (resistance). See methods for measuring and methods for measuring compaction. Recommended methods of assessment include the following.

• Penetrometer - a penetrometer is a portable, easy to use tool. The penetrometer is pushed into a soil and a gauge shows the resistance. Readings greater than 300 psi indicate conditions restrictive to root growth. If more than 50 percent of readings froma field exceed 300 psi, compaction is considered moderate; severe if more than 75 percent of readings exceed 300 psi. Typical cost of a penetrometer is about $200.
• Bulk density - bulk density is a relatively easy to perform measurement but requires determining the water (moisture) content of the soil. Relationships of bulk density to root growth are shown in the adjacent table.

General relationship of soil bulk density to root growth based on soil texture
Link to this table

Soil texture	Ideal bulk densities (g/cm3)	Bulk densities that may affect plantgrowth (g/cm3)	Bulk densities that restrict root growth (g/cm3)
sands, loamy sands	<1.60	1.69	>1.80
sandy loams, loams	<1.40	1.63	>1.80
sandy clay loams, loams, clay loams	<1.40	1.60	>1.75
silts, silt loams	<1.30	1.60	>1.75
silt loams, silty clay loams	<1.40	1.55	>1.65
sandy clays, silty clays, clay loams with 35-45% clay	<1.10	1.49	>1.58
clays (>45% clay)	<1.10	1.39	>1.47

Vegetative growth - Water stable aggregates

Importance: Stable soil aggregates, in the presence of water, is important for water and air transport, root growth, habitat for soil biota, minimizing soil erodibility, protecting soil organic matter, and nutrient cycling.

Assessment: Methods for assessing aggregate stability are somewhat qualitative and different methods do not correlate well. The method selected should simulate field processes likely to affect aggregate stability (e.g. rainfall impact, ponded (flooded) conditions, tillage).

• Sieve or strainer method: The most commonly used method for testing aggregate stability involves placing a soil sample on a nest of soil sieves with screen sizes typically ranging from 1 mm to 45 microns and then moving this nest of sieves up and down in a bucket of water. The more stable aggregates will stay on the top sieve, while less stable aggregates will move through the larger sieves to the finer sieves. Soil stability is assessed by measuring the mass of soil remaining, as a percent of initial soil mass, on the sieve after a specified number of dipping cycles (e.g. 5 cycles). Soils with high aggregate stability will typically retain 50 percent or more of the initial soil mass. This method may represent stability under rainfall.
• Slake test: Dried aggregates are placed into a container filled with water. Assess the aggregates after specified times (e.g. 20 minutes, 2 hours, 20 hours). This method may represent stability under flooded (water immersed) conditions.
• Vibration methods: An ultrasonic probe immersed in water containing soil aggregates vibrates at different vibration amplitudes. Soil stability is assessed after specific time intervals. This method may represent stability under tillage conditions.

Further reading

• Field soil aggregate stability kit for soil quality and rangeland health assessments
• How is soil aggregate stability tested?
• Assessing soil aggregate stability
• Evaluation of methods for determining soil aggregate stability
• Characterization of soil aggregate stability using low intensity ultrasonic vibrations
• Soil aggregate stability

Vegetative growth - Soil contamination

Importance: Soils may contain concentrations of certain chemicals that are toxic to plants. Pollutants of greatest concern include metals (copper, lead, cadmium, nickel, zinc), sodium and chloride from road salt application, pesticides, and some hydrocarbons (e.g. oil, PAHs). Sites with known contamination may contain other pollutants, such as arsenic, but these soils are generally not suitable for stormwater applications without remediation.

Assessment: Risk assessments for metals concentrations in soil are generally based on human exposure, and there is limited information on toxic concentrations for different plants. Nevertheless, most urban soils do not contain chemicals at concentrations which restrict plant growth, although concentrations of these chemicals are typically greater than natural background ([1], [file:///C:/Users/franc/Downloads/environments-07-00098-v2.pdf], [2], [3], [4], [5], [6]). Chemical sampling is expensive, particularly for organic contaminants. An assessment of soil contamination should therefore begin with a site investigation to identify the presence of contaminant sources or historical activities that may have resulted in soil contamination.

• Site visit: Conduct a site visit and determine if any of the following exist at the site - soil stockpiles, tanks or drums, odor(s), visual staining of soils, dead or dying vegetation, and debris that may be a source of contaminants.
• Site review: Conduct a site review consisting of a search for nearby contaminated sites, site historical search to identify past uses, and review of historical aerial photos. Link here for more information and sources.
• Assessment: If a site visit or assessment indicate potential contamination at a site, sampling may be warranted.

Regardless of the results for a site visit and site review, soil sampling is warranted for certain land use settings. The adjacent table provides a summary of potential pollutant concerns for specific land uses. If sampling is warranted, use appropriate sampling and test methods, described on this page.

Pollutants of Concern from Operations (adapted from CWP, 2005).
Link to this table.

Pollutant of concern	Vehicle operations	Waste management	Site maintenance practices	Outdoor materials	Landscaping
Nutrients			X	X	X
Pesticides				X	X
Solvents			X	X
Fuels				X
Oil and grease	X			X
Toxic chemicals		X		X
Sediment		X	X	X	X
Road salt			X	X
Bacteria		X			X
Trace metals	X			X
Hydrocarbons	X			X

Additional reading

• Soil Health Assessment - USDA-NRCS
• Soil Quality Indicator Sheets - USDA-NRCS
• Using Healthy Soils to Manage Stormwater - American Society of Landscape Architects
• Soil Health Fact Sheets – Ocean County, Stormwater Basins
• Soil Health - USDA - NRCS
• Top Healthy Soil Resources - Ocean County, New Jersey, Soil Conservation District
• Soil Health Indicators - University of Minnesota
• Minnesota Office for Soil Health
• Soil Health Project Update - Minnesota Office for Soil Health