Physical properties of soil include color, texture, structure, porosity, density, consistence, and temperature. These properties affect processes such as infiltration, erosion, and biologic activity. These properties also affect suitability of soil for different uses, such as stormwater infiltration, subgrade for roads, and strength for building.
This page provides an overview of soil physical properties, processes they affect, and their affect on use, primarily for stormwater applications.
Soil texture (such as loam, sandy loam or clay) refers to the proportion of sand, silt and clay sized particles that make up the mineral fraction of the soil. Soil texture is determined with one of the following methods.
Other methods are used to determine texture, but these employ qualitative approaches. They include the feel method, ball and ribbon methos, and ball throwing method. These are described here. These methods may be satisfactory for some applications, such as determining if a soil may be suitable for infiltration, but they must be conducted by an experienced person, such as a professional soil scientist.
The following particle size distribution, based on sieve analysis, is commonly used to define soil particles.
Soil texture describes the distribution of these different size particles in a soil. There are twelve soils based on the distribution of sand, silt and clay. The adjacent image displays the soil texture triangle, which assigns soil type based on the distribution of sand, silt, and clay.
Texture affects many soil processes, including infiltration, drainage (water and air distribution), erosion, chemical processes, and biologic processes. These are discussed generally below.
This page provides a nice overview and discussion of soil structure.
Soil structure describes the arrangement and organization of soil particles in the soil, and the tendency of individual soil particles to bind together in aggregates. Aggregation affects water and air transport, which affects the movement of solutes and pollutants and affects biologic activity, including plant growth.
Structure development is influenced by
Soil structure is typically divided into one of the following groups, as illustrated in the adjacent image.
Soil structure affects water and air movement in soil and is therefore important to soil biota. Platy and massive soils have restricted air and water movement, while granular and aggregated soils have enhanced air and water transport.
Soil structure can be altered by human activity, including the following.
Soil density is related to the mineral and organic composition of a soil and to soil structure. The standard measure of soil density is bulk density, defined as the proportion of the weight of a soil relative to its volume. It is expressed as a unit of weight per volume, and is commonly measured in units of grams per cubic centimeters (g/cm3). Bulk density is an indicator of the amount of pore space available within individual soil horizons, as it is inversely proportional to pore space:
Pore space = 1 – bulk density/particle density
where particle density is the weight/volume of the solid material. Typical particle densities are 2.65 g/cm3 for minerals and 1.3 g/cm3 for organic matter.
For example, at a bulk density of 1.60 g/cm3, pore space equals 0.40 or 40%. At a bulk density of 1.06 g/cm3, pore space equals 0.60 or 60%.
Because of the lower particle density of organic matter compared to minerals, soils with higher concentrations of organic matter have lower bulk densities. Typical bulk densities of different soils are illustrated in the adjacent table.
Comparison of bulk densities for undisturbed soils and common urban conditions. (Source: Schueler, T. 2000. The Compaction of Urban Soils: Technical Note #107 from Watershed Protection Techniques. 3(2): 661-665. Center for Watershed Protection, Ellicott City, MD.)
For information on alleviating soil compaction, see Alleviating compaction from construction activities
Link to this table
Undisturbed soil type or urban condition | Surface bulk density (grams / cubic centimeter |
---|---|
Peat | 0.2 to 0.3 |
Compost | 1.0 |
Sandy soil | 1.1 to 1.3 |
Silty sands | 1.4 |
Silt | 1.3 to 1.4 |
Silt loams | 1.2 to 1.5 |
Organic silts / clays | 1.0 to 1.2 |
Glacial till | 1.6 to 2.0 |
Urban lawns | 1.5 to 1.9 |
Crushed rock parking lot | 1.5 to 2.0 |
Urban fill soils | 1.8 to 2.0 |
Athletic fields | 1.8 to 2.0 |
Rights of way and building pads (85% compaction) | 1.5 to 1.8 |
Rights of way and building pads (95% compaction) | 1.6 to 2.1 |
Concrete pavement | 2.2 |
Quartzite (rock) | 2.65 |
Bulk density affects water and air transport in soils. Soils with high densities resist water and air transport. Soils with high density may also impede root growth.
Several human activities affect bulk density. Soils at construction sites are generally compacted as a result of excavation, mixing, stockpiling, equipment storage, and equipment traffic. In addition, exposed subsoil is susceptible to compaction. Clay soils and wet soils are more susceptible to compaction. Even at sites where selective grading is employed, compaction occurs as a result of construction equipment, stockpiling and vehicle traffic (Randrup, 1998; Lichter and Lindsay, 1994).
When soil is compacted, porosity decreases and bulk density increases. Typical increases in bulk density are shown in the adjacent table, with other compacting activities included for comparison. As a result, permeability of air and water in soil decreases, soil water-holding capacity is reduced, and root growth is impeded. On a watershed scale, soil compaction leads to increased runoff and erosion.
Increase in soil bulk density as a result of different land uses or activities.
Link to this table
Land use or activity | Increase in bulk density (grams / cubic centimeter | Source (link to Reference list) |
---|---|---|
Grazing | 0.12 to 0.20 | Smith, 1999 |
Crops | 0.25 to 0.35 | Smith, 1999 |
Construction, mass grading | 0.34 to 0.35 | Randrup, 1998; Lichter and Lindsey, 1994 |
Construction, no grading | 0.20 | Lichter and Lindsey, 1994 |
Construction traffic | 0.17 to 0.40 | Lichter and Lindsey, 1994; Smith, 1999; Friedman, 1998 |
Athletic fields | 0.38 to 0.54 | Smith, 1999 |
Urban lawn and turf | 0.30 to 0.40 | Various sources |
The effects of compaction are difficult to overcome and may persist for decades. Natural processes such as freeze-thaw cycles, animal burrowing, and root growth only slowly diminish compaction. These natural processes are typically limited to the upper foot or two of soil. Even when bulk densities decrease, the original soil structure may not be achieved (Randrup, 1997; Schueler and Holland, 2000).
The following table summarizes results for different activities designed to alleviate compaction. The results suggest compost amendment is an effective method for alleviating compaction, while tillage is considerably less effective. Note however, this is an area of on-going research and some recent studies suggest properly conducted tillage can be effective at reducing compaction. For an example, link here.
Reported Activities that Restore or Decrease Soil Bulk Density
Link to this table
Land use or activity | Decrease in bulk density (gms/cc) | Source |
---|---|---|
Tilling of soil | 0.00 to 0.02 | Randrup, 1918. Patterson and Bates, 1994 |
Spedialized soil loosening | 0.05 to 0.15 | Rolf, 1998 |
Selective grading | 0.00 | Randrup, 1998 and Lichter and Linsy, 1994 |
Soil amendments | 0.17 | Patterson and Bates, 1994 |
Compost amendments | 0.25 to 0.35 | Kolsti et al. 1995 |
Time | 0.20 | Legg et al, 1996 |
Reforestration | 0.25 to 0.35 | Article 36 |
Soil consistence refers to the ease with which an individual ped can be crushed by the fingers. Soil consistence, and its description, depends on soil moisture content. Terms commonly used to describe consistence include the following.