One of the two main conventional soil classification
methods used by a majority of soil scientists in Australia is the Great
Soil Groups (GSG) system (Stace et al., 1968). In this scheme, Australian
soil has been classified into 43 great groups which have been arranged
in seven categories. The Australian Great Soil Groups have been popular
in Australia for many years and many people are familiar with them. Therefore,
the Australian Soil Identification Spreadsheet (ASIS) was designed and
developed to help soil users to allocate an unknown profile quickly as
well as accurately to the GSG. Since some of the 43 original groups are
multiple groupings, it has been expanded to 50.
Fuzzy soil classification
Soil classification, in the traditional sense, is based on the notion that
soil forms discrete, internally homogeneous units, with sharp boundaries.
In this sense each soil unit can be represented by a central idea known
as a typical or representative profile. This model implies that the predicted
value of a soil attribute at any unsampled area is either the value for
the typical profile or the mean value for the soil unit.
The problem of dealing with undefined classes and vague boundaries
has led to fuzzy soil classification in which soil may belong totally,
partially or not at all to soil classes. In practice, the extent of soil
membership in any class is permitted from zero (no membership) to one (membership
in one class only). The main feature of this system of classification is
the grouping of soil individuals into classes where boundaries are not,
should not or can not be, exactly defined. These diffuse classes are known
as continuous classes and the system itself is called continuous classification
(McBratney & De Gruijter, 1992). Allocating unknowns to fuzzy and continuous
soil classes is dealt with in detail by McBratney (1994).
Advantages of this system
This system allows soil scientists to check the results of soil identification
through the membership allocation; the greater the membership, the stronger
the linkage to a great soil group. As this system is more flexible than
conventional ones, it can transfer more and better information to users.
Fuzzy soil classification is a continuous, quantitative or objective
procedure in which the classes are defined in terms of membership and based
on many properties simultaneously (polythetic). Additionally, as
for qualitative attributes such as soil structure, this system can accommodate
these subjective assessments. No special expertise is required, except
for a general knowledge of soil description.
The ASIS program
The ASIS is based on the fuzzy k-means with extragrades
algorithm. Fuzzy k-means with extragrades has been applied to permit
variation in the distance dependence for membership in the outlier group
recognised by De Gruijter & McBratney (1988).
The implementation on the Macintosh and PC makes
the technique for generalised fuzzy k-means available for soil profile
identification for the first time to everyday users. ASIS requires
an Apple Macintosh or Windows compatible PC with Microsoft Excel version
5.0 or higher installed.
Download ASIS
Using ASIS
ASIS requires inputs to be coded and soil colour attributes
transformed in a particular manner (Mazaheri et al., 1995a). Twenty
attributes are needed: topsoil and subsoil texture for texture profile;
topsoil salinity; subsoil salinity; topsoil organic matter %; subsoil pH
(1:5 H2O); subsoil structure; subsoil mottling; subsoil clay %; bleaching
of A2 (E) horizon (if present); concretions; crust; hardpan; topsoil calcium
carbonate; subsoil (pedological) calcium carbonate; subsoil gypsum; pedological
subsoil; alluvial layer; parent material and subsoil colour.
For allocation of the profile to one of the texture
profile classes of uniform, gradational and duplex (Northcote, 1984), the
topsoil, midpoint (A2, A3, A/B or B1, if present) and subsoil texture should
be determined. ASIS can allocate the profile automatically to the texture
profile. Topsoil and subsoil salinity should be expressed in dS m–1 in
a 5:1 water:soil extract. Acidity or pH should be measured in 1:5 soil:water
ratio. As organic matter in soil is not usually measured, it can be calculated
by approximate conversion that assumes soil organic matter contains generally
57 % carbon. Therefore,
% O.M.= % O.C. ´
100/57
Moist soil colour is quantified and transformed automatically
within the spreadsheet, provided the Munsell hue, chroma and value are
entered. The final result is an allocation to one or more GSG. The membership
values are displayed and may be printed out.
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Designed by: Budiman
(c) 1998