A.N.Morozov
SOIL-MELIORATIVE ZONING OF AN AREA
The soil-meliorative
zoning system in the way as it stated below was born in the Soil-Meliorative
Investigations Department of the former "Sredazgiprovodkhlopok"
(Central Asian State Design Institute of Water and Cotton) under the
direction of Vladimir Rikhardovich Shredder in 1965-1970 years. That
shaped thus due to the production need. That was a period of mass
development of virgin lands for irritation. One had exactly and competently
to distinguish soils by their properties for designing proper reclamation
measures. As far as competently and bona fide those designs were carried
out is a question of another issue.
One should note that neither reclamation of new lands nor meliorative
state monitoring of old-irrigated lands, whatever way made, cannot
be realized correctly without basing on soil-meliorative zoning, which
takes into consideration (synthesizes) basic climatic, geomorphologic,
hydrogeologic, lithologic, hydrochemical, and soil-meliorative characteristics
of a territory. All investigations conducted without taking into consideration
soil-meliorative zoning can be likened to an attempt of creating a
thermonuclear bomb by physicists who have secondary school level education.
Soil-meliorative zoning is a system that allows finding out in what
specifically diverse soil in one region differ one from another and
in what similar soils in different regions are alike.
At soil-meliorative zoning, as stated above, the following soil constituent
factors are taken into account, which determine conditions for irrigation
and reclamation:
* climate;
* hydrogeological conditions;
* meliorative-farming conditions;
* lithologic-geomorphologic structure.
Differences of climatic conditions depend on latitudinal location
and vertical zoning. For practical purpose of water consumption rating,
the Central Asia territory divides into three zones: North (N), Central
(C), and South (S), each of those subdivided into north (I) and south
(II) parts. Distinguishing soil-climatic zones and belts is based
on quantitative indices of precipitation amount, temperature mode,
and air humidity.
In each climatic zone, belt-altitude zones are distinguished by vertical
zoning. Their description is given Table 1, where, also, quantitative
characteristics are cited in the form of natural moisture factors
(Mf) that is the generalizing index of local thermal and water resources
and are found via the formulae:
Mf =
( + Ws)/
here, PO - average many-year total of precipitation for a year's period
with air temperature higher than + 5 Co, mm;
Ws - moisture reserve in a soil layer of 1 m at the begging of the
designed period, mm;
Eo - evaporability during the designed period, mm.
Vertical zoning belts are distinguished by moistening conditions in
a winter-spring period. Precipittion quantity from B belt to G belt
increases and the natural moistening period become longer. A summer
period and first autumn months are equally dry and a littlie differ
by the temperature mode.
Table
1. Zoning of Uzbekistan territory by the moistening factor
|
Belt
|
Type
of soil constituent (automorphic series)
|
Moistening
factor
|
Deserts
|
|
Deserted
|
0.05
- 0.10
|
1
|
Transitional
to a sierozem belt
|
0.10
- 0.15
|
Ephemeral
steppes
|
B
|
Sierozem
Light
sierozems
|
0.10
- 0.20
|
C
|
Sierozem
Typical
sierozems
|
0,15
- 0,25
|
Motley
grass steppes
|
D
|
Sierozem
Dark
sierozems
|
0,25
- 0,30
|
Meliorative
estimate of hydrogeological conditions is based on hydrogeological
and soil-meliorative zoning, as a criterion for which is groundwater
balance (present or designed) that is determined by the conditions
of their feed and discharge (flow-out, transpiration, and evaporation).
With an allowance for these indices, the following hydrogeological-meliorative
regions are distinguished:
* a - secured outflow and transit of groundwater at deep location,
not influencing on soil constituent;
* a1 - secured local groundwater outflow due to relief ruggedness;
* b - intensive external inflow, backwater, and pinching-out of groundwater
with steady close location;
* c - difficult inflow and outflow of groundwater with unsteady location
depth and regime not depending on local conditions.
In the regions "a" and "a1", soil-meliooprative
situation is determined by relief conditions and lithologic composition
of soil constituent strata. Their distinguishing is important only
from the genetic standpoint, but it in no way has an effect on water
losses to evaporation and transpiration.
In the regions "b" and "c", main differences are
conditioned by water-cycle type (amount and activity of inflow and
outflow) of groundwater and hydrochemical zoning related to that.
Territories are differentiated subject to groundwater location and
mineralization. Areas with flesh groundwater are marked with indices
"b" and "c"; with mineralized groundwater (more
than 5 g/l) with "b1" and "c1" in accordance with
belonging to one or another hydrogeological-meliorative region.
The most steady in the complex of factors determining capacitive characteristics
of soil moisture in relation to water and soil moisture's dynamic
characteristics are properties of a soil constituent stratum correlated
to considerable extent with its granulometric structure:
* aeration degree;
* water permeability;
* specific water retention;
* capillary properties;
* thermal mode; and others.
Sand and loamy sand soils have favorable air and thermal mode, are
water permeable, but have low moisture capacity. Loamy soils have
high moisture capacity and poor water permeability, bad water yield,
high swelling, and adverse thermal features.
Loamy soils, being in middle, are the best by the properties and composition.
They have favorable air and thermal modes, good water permeability,
high moisture capacity, and mobility of soil moisture.
Differentiation of the irrigation regimes five principal groups of
soil constituent strata are marked out, which noticeably differ by
indices of water-physical properties:
* 1 - sand;
* 1a - low-thick, highly stony;
* 2 - loamy sand;
* 3 - light and medium-loamy;
* 4 - medium-loamy (dense) and heavy loamy;
* 5 - loamy.
Averaged values of soils? water-physical property indices characterizing
the marked groups are presented in Tables 2 and 3.
Table
2. Water-physical characteristics of main types of ground
Soil
constituent stratum
|
Volume
moisture at values of pF=lg(P,cm):
|
0,0
|
1,0
|
2,0
|
2,5
|
3,0
|
3,3
|
3,7
|
4,0
|
4,3
|
4.5
|
Sand
|
0,44
|
0,41
|
0,24
|
0,10
|
0,07
|
0,06
|
0,04
|
0,04
|
0,03
|
0,03
|
Loamy
Sand
|
0,44
|
0,43
|
0,32
|
0,22
|
0,14
|
0,10
|
0,07
|
0,05
|
0,05
|
0,04
|
Light
Loamy Soil
|
0,44
|
0,44
|
0,37
|
0,28
|
0,20
|
0,16
|
0,12
|
0,09
|
0,08
|
0,07
|
Mean
Loamy Soil
|
0,46
|
0,45
|
0,37
|
0,29
|
0,22
|
0,18
|
0,14
|
0,11
|
0,09
|
0,08
|
Heavy
Loamy Soil
|
0,46
|
0,44
|
0,38
|
0,32
|
0,25
|
0,21
|
0,16
|
0,13
|
0,10
|
0,08
|
Light
Loam
|
0,46
|
0,45
|
0,43
|
0,40
|
0,35
|
0,30
|
0,23
|
0,19
|
0,15
|
0,13
|
Table
3. Averaged characteristics of soil constituent strata of various
granulometric structure soil constituent stratum
Soils
|
Concentration
of particles less than 0.01 mm, %
|
Volume
weight, g/cm3
|
Flirtation
factor Kf, m/day
|
Cationic
exchange capacitance, mg eqv/100 g
|
Sand
|
9
|
1.5
- 1,6
|
1.00
- 3,00
|
2
- 4
|
Loamy
Sand
|
9-15
|
1.4
- 1.5
|
0.50
- 1.00
|
4
- 6
|
Ht LoamLigy Soil
|
15-35
|
1.3
- 1,4
|
0.25
- 0.50
|
6
- 8
|
Mean
Loamy Soil
|
35-50
|
1.4
- 1,5
|
0.07
- 0,25
|
8
- 10
|
Heavy
Loamy Soil
|
50-60
|
1.4
- 1.5
|
0.02
- 0.07
|
8
- 12
|
Light
Loam
|
60-72
|
1.61
- 1,7
|
0.05
- 0.01
|
10
- 15
|
Soils
of heterogeneous lithologic structure by moisture capacity and conditions
of soil moisture expenditure are equated to the mentioned main groups
in the following way:
* to the 1st group belong low-thick (0.2-0.5 m) loamy ones on sand-pebble
deposits and on gypsums, and, besides, to the 1a group belong very
low-thick, highly stony ones;
* to the 2nd - medium thick (0.5-1.0 m) loamy on sand-pebble deposits
and on gypsums;
* to the 3rd - loamy, becoming lighter downward;
* to the 4th - loamy, becoming heavy downward;
* to the 5th - highly stratified with availability of loam.
Table
4. Hydro-module zoning by "Sredazgiprovodkhlopok" (V.R.Shredder,
1970)
Groundwater
table depth, m
|
Granule
composition
|
Sand
|
Loamy
sand
|
Light
and medium loamy soils |
Medium
and heavy loamy soils |
Loamy
|
>
3
|
I
|
II
|
II
|
III
|
III
|
2
- 3
|
IV
|
IV
|
V
|
V
|
V
|
1
- 2
|
VI
|
VI
|
VII
|
VII
|
VII
|
0,5
- 1,0
|
VIII
|
VIII
|
IX
|
IX
|
IX
|
Transition from the above-presented scale adopted by "Sredazgiprovodkhlopok"
in 1970 to a "corrected" scale (used now for the purpose
of most adequate reflection of natural conditions met when drawing
maps of hydro-module zoning) is shown in Table 5.
Table
5. The "corrected" scale adopted at soil-meliorative zoning
and its conformity with the V.R.Shredder's scale.
Soil
characteristics
|
Corrected
scale
|
Zoning
by V.R.Shredder.
|
Automorphic
soils (groundwater table GWT > 3 m)
|
Low-thick
(0.2-0.5) mean stony of diverse granulometric composition on
sand-pebble deposits and on gypsums; low-thick
|
I
|
I
|
Thick
medium, heavy loamy and loamy
|
I
|
I
|
Medium-heavy
low stocky, different in granulometric structure on sand-shingle
sediments and gypsum; heavy loamy sand and low loamy.
|
II
|
II
|
loamy
sand and light loamy
|
III
|
III
|
Half-hydromorphic
soils (GWT 2-3 m)
|
Thick
sand and loamy sand, as well as low and mean thick of diverse
granulometric composition
|
IV
|
IV
|
Thick
light and mean loamy, homogeneous heavy loamy, becoming light
downward
|
V
|
V
|
Thick
heavy loamy and loamy dense homogeneous, different by granulometric
composition, stratified by structure
|
VI
|
V
|
Thick
sand and loamy sand, as well as low and mean thick of diverse
granulometric composition
|
VII
|
VI
|
Hydromorphic
soils (GWT 1-2 m)
|
|
|
Thick
light and mean loamy, homogeneous heavy loamy, becoming light
downward
|
VIII
|
VII
|
Thick
heavy loamy and loamy dense homogeneous, different by granulometric
composition, stratified by structure
|
IX
|
VII
|
In this
form, soil-meliorative zoning faces today many problems, which are
to be solved by the next generation of scientists. This is, first
of all, attaching the quantitative indices to many qualitative ones
stated above. Who is familiar with the works by V.R.Shredder will
note that we tried in tables 2 and 3 to add such indices related to
soil physics, but, there is plenty of works to be done. There are
a number of unknown indices, for instance, we can indicate the followings:
- degree of drainage (provision by natural or artificial drainage);
- dependence of soil leaching ability on its granulopmetric composition
and state of the soil horizon.
- Influence of soils? pore space structure on regularities of absorbency
and capillary rise; and so forth.
How
to get in touch with us?
Return
to the main page
|