2.1 Development of Soil Standards and Agricultural Land-use Guidelines
in Uganda
Early attempts to establish land-use
management guidelines were preceded by land inventories to establish
the status of the Uganda soil resource base. Resource inventories started
in 1933 (Martin, at Kawanda) and the limited results were embodied in
the Provisional Soil Map of East Africa"
compiled by Milne (1935). Between 1935-1954 several attempts were made
to improve the first soil map so that appropriate land-use management
guidelines (especially for agricultural land use) could be put in place.
The first
detailed country-wide resource Inventories were carried out during the
reconnaissance survey (1955-1960) by the Soil Unit at Kawanda. Geomorphological
surfaces on which the soils were formed was a major criterion used in
soil survey and classification and the mapping unit employed was the
series and soil catenary associations. Most of the present Soil Conservation
Bye-Laws and Land Management Laws were based on information gathered
during this survey.
The survey recognized 138 soil mapping
units which were initially published in black and white soil maps at
a scale of 1:500,000. These were later revised to produce more detailed
17 coloured soil maps at a scale of 1:250,000. The findings of the survey
were published in six volumes of memoirs.
The memoirs contain a wealth of information
which has partly been the basis for the establishment of critical values
(thresholds) for soil chemical and physical parameters. Laboratory data
on selected pedons are given, outlining
soil texture, exchangeable bases, soil reaction, organic carbon, and
available phosphorus. Comments are made on some nutrient values, whether
they are very high or too low for normal crop production.
The memoirs grouped the soils of Uganda
according to their suitability for major cash crops in 1959; namely,
coffee, cotton, tobacco, tea, sugarcane, and cocoa. Additionally there
were soil groupings for suitability for plantains. For each crop the
soils were arranged in three categories:
eminently suitable,
suitable,
barely suitable.
Unsuitable soils were not mentioned.
2.1.1 Soil Fertility and Productivity
Rating
The report rated Ugandan soils in 1959,
for their fertility and productivity. It pointed out that the fertility
of the red tropical soils in Uganda was confined in the top-soil which
is usually 23-36 cm deep. The report pointed out the loss of nutrients
in the top layer and structure destruction as the most serious causes
of soil degradation in Uganda.
It gave some guidelines on the management
of soils by farmers in order to reduce soil degradation. The guidelines
and recommendations include:
grass-rest under elephant grass as
a management practice for building up fertility and productivity of
the soils;
contour planting and cultivation, contour paspalum- grass bunding,
contour strip cultivation on slopping land;
application of farm yard manure; and,
application of some selected chemical fertilizers.
These standard practices are valuable
in controlling loss of soil fertility. Their enforcement must be urgently
reactivated.
2.1.2 Drainage and Irrigation
The report rated internal drainage of
practically all upland soils as being free-draining. It indicated that
bottom lands were water-logged all through the year or some months of
the year, and pointed out that most of the bottom-lands could be safely
drained. The report, however, warned against draining and irrigating
the acidic and leached bottom-lands in southern Uganda. The richer soils
of the Rift Valley, the Sebei and Karamoja plains were rated as
suitable for irrigation if water were available.
2.1.3 Standards for Plant Nutrients
The report classified soil concentration
of individual plant nutrients which comprise soil fertility at three
levels:
very high
high
low
For each of the plant nutrients considered,
Ugandan soils were grouped on the basis of which level of nutrient they
belong to.
Between 1960-1970, considerable effort
was put in the establishment of minimum chemical standards for soil
fertility and productivity rating. Foster (1971), working at Kawanda,
developed routine methods for soil chemical
analyses and these were accompanied by the minimum chemical standards
that have formed the basis for the present nutrient management guidelines
for the whole country
Magunda (1994), proposed soil physical
standards for the intensive banana-coffee-lake-shore farming system.
These standards have since been validated in the other agro- ecological
zones. These standards are to serve as an early warning signal of reduced
productive capacity of soils or
degradation. Specific physical parameters and threshold values were
suggested for the surface layer and sub-soil. Standards should be viewed
as a range of conditions where balance between exploitation and soil
formation have moved away from a desired balance (Leonard et al 1990).
Consequently the goal of soil quality standards is to maintain, restore
or enhance the inherent long-term soil productivity.
2.2 Development of Soil Standards
by Other Countries and Agencies
The demands for the kind of soil map
and data vary, from one user to another. Some users are searching for
the most suitable soil for growing particular crops. Others are interested
in management and improvement inputs that puts their land to the most
efficient use. There are yet other soil data users who need the data
for locating home sites, waste disposal sites, roads, highways, and
legislative land-use controls.
Significant effort has been made to develop
soil standards at international level. The following are of particular
importance. Those measurable soil properties that are important for
assessing the soil plant root environment are reported by Bartelli,
(1979) as:
effective depth of root ramification zone;
texture;
organic matter content;
salt content;
cation exchange capacity;
base saturation;
mineral content;
permeability;
saturated and unsaturated conductivity;
soil wetness (drainage); and
depth to water table and available water holding capacity.
Soil Survey Manual (Soil Survey Staff,
1951) analyzed land features that influence soil behaviour as:
slope;
flooding;
wetness;
rockiness; and,
geomorphological position.
Slope is important in that it influences
soil erodibility and water run-off, equipment manipulation, street lay-out,
under-ground conduits, harvesting of wood products and land levelling
(Bartelli, 1979).