Environmental Engineering Reference
In-Depth Information
Table 7.4.
Clay mineral identification from the environment (Ingles and Metcalf, 1972).
Dominant clay component (1)
Observation
Turbid water of strong yellow-brown to red-brown
Montmorillonites, illite plus soil
colour
salinity
Clear waters
Calcium, magnesium or ironrich soil,
highly acid soil sands
Clear waters with a bluish cast
Non-saline kaolins
Erosion gullies and/or field tunnelling in the natural soil
Saline clays, usually montmorillonites
As above, mild erosion
Kaolinites
Landslips
Kaolinites, chlorites, montmorillonites, illites
Surface microrelief (gilgai)
Montmorillonites
Country rock type granitic
Kaolinites, micas
Country rock type basaltic, poorly drained topography
Montmorillonites
Country rock type basaltic, well drained topography
Kaolinites
Country rock type sandstones
Kaolinites
Country rock type mudstones and shales
Montmorillonites or illite, often soil salinity
Country rock type limestone
Alkaline montmorillonites and of very
variable properties
Country rock type recent pyroclastics
Allophanes
Note: (1) The dominant component of the soil may be silt or sand sized eg. for granites, sandstones.
- The presence of cloudy water in farm dams and puddles of water after rain indicates
dispersive soils.
One can infer the clay mineralogy from such observational techniques. Some guidelines
are given in Tables 7.4 and 7.5 reproduced from Ingles and Metcalf (1972).
The geology of the area can also be a guide to dispersivity.
Sherard and Decker (1977) indicate that:
-
Many dispersive clays are of alluvial origin. (The authors' experience is similar but
there are many non dispersive alluvial clays. Some slopewash clays are also dispersive);
-
Some soils derived from shales and claystones laid down in a marine environment are
also dispersive;
-
Soils derived from weathering of igneous and metamorphic rocks are almost all non
dispersive (but may be erodible, e.g. silty sand derived from grandiorite);
-
Soils with a high organic content are unlikely to be dispersive (this needs to be treated
with caution, since many “black cotton” soils are dispersive).
7.7
USE OF DISPERSIVE SOILS IN EMBANKMENT DAMS
7.7.1
Problems with dispersive soils
Dispersive soils are a major contributing factor to piping failure of embankment dams,
particularly for small homogeneous dams constructed without filters and often with poor
construction supervision. This view is widely held e.g. Sherard et al. (1976a, b, 1985).
However, failures do occur in structures which are reasonably well engineered. The main
contributory factors are:
-
The presence of dispersive soils in the embankment or foundation;
-
Poor compaction of the soil, i.e. to a low density ratio and/or dry of optimum water
content;
-
Poor compaction of soil around pipes or conduits which pass through the embankment;
 
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