
Soil management, or soil conservation, deals with some aspect of protecting soil resources and using soils in a sustainable manner. Effective soil conservation in agriculture hinges on five basic principles:
This publication focuses on the first three
principles. Additional information on items #4 and #5
are found in the Soil Fertility Guide, Field Crop
Production Guide and Guide to Crop Protection
published by Manitoba Agriculture, Food and Rural
Initiatives and in other agronomy-related publications.
To fully appreciate and understand the principles of
soil management, one must understand the soil itself.
The first part of the guide deals with how soils are
formed and classified. The latter section uses these
principles to identify certain soils (under certain
conditions) that would benefit the most from a
particular soil conservation practice.
Soils comprise the uppermost layer of the earth’s surface. They were developed by the action of climate on rock and sediments under the influence of organic life. The first interest in the soil was related to its ability to produce plants for food and fibre. In this context, soil is defined as the collection of natural bodies on the earth’s surface supporting or capable of supporting plants (Brady, 1984).
Soils are required for food production and for filtration of water. However, only 1/16 of the earth’s surface has soil that is suitable for growing crops. Of the 160 million acres (65 million hectares) in Manitoba, only 19 million acres (7.7 million hectares) have potential for agriculture. Much of this land has been settled over time, and is either being lost to urbanization or being mismanaged so that erosion, salinity, compaction and organic matter losses have made the soil less productive. Over a 10 year period from 1991 to 2001, approximately 36,600 acres (14,640 hectares) of land in Manitoba has been subdivided into building lots for non-agricultural land uses (Land Use Planning Group, 2003).
Table 1.1 Relative area of various segments of Manitoba
| Million Acres (approx.) |
Million Hectares (approx.) |
|
| Total Area - Manitoba | 160 | 65 |
| Total Land Surface - Manitoba | 136 | 55 |
| Total Land Area - Agro-Manitoba | 26 | 10.5 |
| Land in Farms - Agro-Manitoba | 19 | 7.7 |
| Improved Land (Crops, Fallow, Pasture) | 13 | 5.3 |
| Unimproved Pasture | 4 | 1.6 |
| Other (e.g. yard sites, etc.) | 2 | 0.8 |
(Source: Manitoba Agriculture Yearbook 2003)
Table 1.2 Land use data within agro-Manitoba as based on
satellite imagery from 1999-2002
(Manitoba Conservation -
Manitoba Remote Sensing Centre, 2002).
| Land use | Total (ac) | Total (ha) |
| Agricultural Cropland | 12,161,607 | 4,921,648 |
| Trees | 6,279,339 | 2,541,167 |
| Water Bodies | 620,708 | 251,193 |
| Grassland/Rangeland | 6,001,550 | 2,428,751 |
| Wetlands | 2,222,681 | 899,491 |
| Forages | 1,038,032 | 420,078 |
| Urban & Transportation | 828,344 | 335,220 |
| Total | 29,152,261 | 11,797,548 |
"In the past, many industrial developments were put on poor soils because the land was (inexpensive), but in the future information on soils and the environment must be considered much more carefully to avoid repeating past mistakes. Many of our (waste disposal) problems can be solved and mistakes avoided by increased use of soil maps together with other environmental information." (Olson, 1984)
The first step in sustainable soil management is ensuring that the soil will support the land use activity. For example, only the better agricultural soils in Manitoba will support grain and vegetable production, while more marginal agricultural soils will support forage and pasture-based production. For this reason, agricultural development should only occur in areas where the soil resource will support the agricultural activity. The only way to do this is to understand the soil resource that is available.
Soils vary significantly in their properties. They may be
deep in some places, shallow in others, black or gray in colour,
sandy or clayey in texture. Although the soil mantle covering
Manitoba is far from uniform, all soils have some common
factors. For example, all soil is a mixture of organic and
mineral material plus water and air. While the major components
remain the same, the proportion of each component in this
mixture varies from soil to soil.
Every farm may consist of several types of soil. To date, over
1,000 different soil types have been recognized in Manitoba,
about 550 of which can be found in agro-Manitoba. They are not
scattered randomly, but occur in definite geographic areas and
in certain patterns. Significant differences set apart the soil
of a poorly drained pothole from the adjacent well-drained ridge
or hilltop while relatively small differences occur between
adjacent soils on level fields of uniform texture.
Soils are a product of their environment. The addition, loss, translocation and transformation of materials in soils determine the way soils form. Soils form and progressively develop under the influence of several environmental factors.
Soils form and progressively develop under the
influence of four soil forming factors acting
over time:
1. Parent Material - the original material from which soils develop. It is based on type of bedrock and method of deposition. In Manitoba, soils contain some combination of granite, limestone or shale. These rocks break down over time through weathering to form sand (from granite) or clay (from shale). Limestone can break down into sand, silt and clay-sized particles. |
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Figure 1.1 Distribution of types
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Table 1.3 Modes of deposition and examples of their location
| Mode of Deposition | Description | Examples |
| Till | Glacier-deposited material; usually stony, mixed material | Interlake Southwest Manitoba |
| Lacustrine | Lake-deposited material; usually well-sorted, non-stony material | Red River Valley |
| Fluvial | River or stream-deposited material | Assiniboine River Valley Pembina Valley |
| Outwash | Gravels deposited by rapidly flowing waters | Brandon area Birds Hill Park |
| Eolian | Wind-deposited materials (sand dunes) | Spruce Woods Park Sandilands Park |
| Organic deposits | Accumulation of peat from dead vegetation in poorly drained sites in cooler climatic regions | North Interlake Southeast Manitoba |
2. Relief - The land surface
of Manitoba is not perfectly flat. In Manitoba
landscapes, areas of higher and lower elevation can
be found within a given field and across the
province. These areas respond differently to the
addition of moisture through precipitation.
Water tends to run off higher areas and collect in
lower areas. As a result, the tops of knolls are
usually the driest part of the landscape, with thin
stands of vegetation and a shallow layer of topsoil.
Erosion also removes topsoil from knolls and steep
slopes. Deeper soils develop on midslopes and lower
slopes which receive and retain most of the
precipitation, resulting in heavier stands of
vegetation. Soils on lower slopes and in depressions
may have the deepest topsoil because of the
deposition of eroded material from upslope. Excess
water in depressional areas causes ponding,
stimulates the growth of aquatic vegetation and may
contribute to saline conditions.
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Figure 1.2 Effect of relief on water movement and the development of soils |
In southwest and southern Manitoba where temperatures are moderate and fairly large amounts of water are evaporated from the surface, the native vegetation is mainly grass. Most of the biomass from grassland vegetation is found below the surface, resulting in the addition of large amounts of organic matter into the soil, producing black topsoil.
In the cooler, more humid conditions of eastern and
central Manitoba, where evaporation is less, the native
vegetation is trees. Most of the biomass from forest
vegetation is found on the surface, from leaf fall, stem
decay and decomposition of mosses. Little organic matter is
incorporated into the soil, resulting in grey topsoil.
Human activities such as agriculture have influenced soil
formation by modifying large areas of natural vegetation
through cultivation. Removing vegetative cover increases
water runoff and alters the moisture and temperature status
of the soil. Removing excess water through drainage also
changes the moisture conditions in the soil. The removal of
natural vegetation and mixing of soil layers can adversely
alter the properties of the soil. However, through proper
management of soil conservation practices, soil erosion,
degrading soil quality and loss of natural fertility can be minimized.
| 1. Texture Soil texture is the relative proportion of sand, silt and clay particles. The texture of a soil cannot be altered. In agriculture, soil texture is determined by measuring the size and distribution of particles less than 2.0 mm in diameter. Particles larger than 2.0 mm in diameter, such as gravel and stones, are included in the textural description only if present in significant amounts (e.g. gravelly sand (GrS)).
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| Figure 1.4 Particle size comparison |
| Sands (S), loamy sands (LS) and sandy loams (SL) are
dominantly composed of sand particles. For these soil textures,
sand particles are further broken down into subclasses:
Very coarse sand (VCoS) = 2.0 - 1.0 mm in diameter
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Figure 1.5 Soil textural triangle |
Table 1.4 Textural groups and classes
| Texture Group |
Texture Class |
Texture Class Symbol |
| Very Coarse | Very coarse sand | VCoS |
| Coarse sand | CoS | |
| Medium sand | S | |
| Coarse | Fine sand | FS |
| Loamy coarse sand | LCoS | |
| Loamy sand | LS | |
| Loamy fine sand | LFS | |
| Moderately Coarse | Very fine sand | VFS |
| Loamy very fine sand | LVFS | |
| Coarse sandy loam | CoSL | |
| Sandy loam | SL | |
| Fine sandy loam | FSL | |
| Medium | Very fine sandy loam | VFSL |
| Loam | L | |
| Silt loam | SiL | |
| Silt | Si | |
| Moderately Fine | Sandy clay loam | SCL |
| Clay loam | CL | |
| Silty clay loam | SiCL | |
| Fine | Sandy clay | SC |
| Silty clay | SiC | |
| Clay | C | |
| Very Fine | Heavy clay (>60%) | HC |
2. Structure
Soil structure refers to the way in which soil particles cling
together to form aggregates. Clay particles tend to cling
tightly together and resist separation more than sand particles.
As organic matter decomposes to humus, a variety of compounds
are released which “glue” soil particles together.
When individual soil particles are aggregated, they form larger,
relatively stable primary structures. If the individual
aggregates are distinct and clearly separated from one another,
the soil is said to have well-developed structure. But if the
fine clay and organic particles are dispersed throughout the
soil, the result may be a poorly developed structure. If there
are no visible aggregates at all, the soil is structureless,
described as either single grain (as found in some sands) or massive (as found in some heavy clays).
Types of soil structure include: prismatic, columnar, angular
blocky, subangular blocky, platy and granular. Most agricultural
soils have either blocky or granular structure. Forest soils
usually have a platy structure at or just below the soil
surface. Prismatic and columnar structures develop in soils with
significant amounts of sodium present in the subsoil.
Structure has a significant effect on soil water properties and
the ability of a soil to resist erosion. Good soil structure
increases porosity, aeration, drainage and permits easier root
penetration, all of which are important on soils with limited
internal drainage, such as clays. Conversely, poor soil
structure in the topsoil produces hard, massive clods, which
makes a poor seedbed for germinating crops. Poor structure in
the subsoil results in dense, compact properties which limit
root and moisture penetration.
The natural structural properties of surface soil horizons can
be changed by tillage, crop rotation, artificial drainage and
applications of manure. As a result, it is important to maintain
a desirable soil structure to ensure optimum crop production.
For example, massive clay soils are difficult to till when dry
and are not easily accessible for field equipment when wet.
Poorly structured sandy soils are easily pulverized by tillage,
making them prone to erosion.
3. Colour
Soil conditions such as drainage and salinity, and constituents
such as organic matter, iron and carbonates, impart
characteristic colours to the soil profile. These colours are
measurable and are used as part of the soil classification
criteria. Light coloured topsoil indicates either low organic
matter content or a concentration of carbonates or soluble
salts. Dark coloured topsoil, by contrast, indicates high
organic matter content. Subsoil colour is an indicator of
drainage that is often more reliable than the actual moisture
conditions at the time a soil is examined. Bright colours, such
as light brown, yellow or reddish subsoil, is characteristic of
a well-drained profile. Dull grey, bluish-green or rust colours
indicate a poorly drained profile.
4. Bulk Density
Bulk density is the apparent density of a soil, measured by
determining the oven-dry mass of soil per unit volume. The
volume of soil is determined using sampling cores and is
measured before soil is oven-dried to avoid any changes in
volume due to drying. Bulk density is usually expressed in g/cm3
or Mg/m3.
Bulk density tends to be higher in sandy soils than in clays. A
typical clay soil has a bulk density around 1.1 g/cm3; a sandy
soil’s bulk density is approximately 1.3 g/cm3; compacted soils
may have a bulk density as high as 1.8 g/cm3.
5. Drainage
Soil drainage is the speed and extent of water removal from the
soil by runoff (surface drainage) and downward flow through the
soil profile (internal drainage). It also refers to the
frequency and duration when the soil is not saturated.
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Figure 1.6 Soil drainage classes on four sandy soils
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Drainage classes:
In general, drainage is primarily influenced by soil texture and relief. Coarse-textured, porous soils allow excess water to pass through the soil whereas finer-textured, compact clay materials tend to restrict water movement. Nevertheless, texture and drainage are independent factors, with relief having a greater influence on the drainage class of a soil than its texture. For example, sands in low-lying areas with high water tables are poorly drained, and clays in relatively higher portions of the landscape can be well-drained. |
6. Calcium Carbonate Content
Calcium carbonates (and, to a lesser extent, magnesium
carbonates) are common to most agricultural soils in
Manitoba. They are derived mostly from fragments of
limestone rocks. Over time, carbonates dissolve and move in
the soil water.
The calcareous nature of Manitoba soils is basically what
maintains their neutral to high pH. Adequate levels of
calcium and magnesium, both essential nutrients for plant
growth, are usually present in calcareous soils. Since most
of the agricultural soils in Manitoba are calcareous, the
addition of lime to raise the pH is not a required practice.
Soil surveyors use dilute hydrochloric acid (HCl) to check
for the presence of carbonates. Calcium and magnesium
carbonates react with HCl to produce carbon dioxide (CO2)
which can be identified by bubbling and fizzing in the area
where the HCl was applied. The greater the carbonate content
of the soil, the more aggressive the reaction is with HCl.
The depth at which dilute HCl reacts with calcium carbonate
(CaCO3) gives an indication of internal soil drainage and
soil development. Over time, soils with good internal
drainage have had significant amounts water infiltrate and
percolate through the soil. Provided they have not been
affected by wind, water, or tillage erosion, they will be
free of CaCO3 in the surface layer and the subsoil layer
below the surface horizon. In these soils, dilute HCl will
not fizz until it comes into contact with the CaCO3 below
the subsoil layer. With the exception of leached micro
depressions, less infiltration and percolation of water in
imperfectly drained soils is reflected in the presence of
CaCO3 at the surface or in the subsoil layer below the
surface layer. Very low infiltration and percolation of
water in poorly drained soils (with the exception of leached
depressions) usually results in calcareous (CaCO3) surface
layers. Therefore, dilute HCl will fizz nearer to or at the
surface in imperfectly and poorly drained soils.
Calcium carbonate content is expressed as the “calcium
carbonate equivalent,” and can range from 0% in extremely
leached soil profiles to over 40% in the high lime tills
found in the Interlake region of Manitoba.
Soil Horizon - a layer of soil running approximately parallel to the land surface and differing from vertically adjacent layers in terms of physical, chemical and biological properties such as colour, structure, texture, pH, etc.
Repeating or alternating layers of different colours, textures, etc. in the soil profile are referred to as a stratified profile. This is referred to as a cumulic profile in soil survey reports.
Table 1.5 Soil horizon designations
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Organic Horizons - contain more than 30% organic matter by weight |
||
| O | an organic horizon developed mainly from mosses, rushes and woody materials | |
| Of | fibric horizon (least decomposed) | |
| Om | mesic horizon (intermediate decomposition) | |
| Oh | humic horizon (most highly decomposed) | |
| LFH | organic horizons developed from leaves, twigs and woody materials | |
| Mineral Horizons - contain less than 30% organic matter by weight | ||
| A - surface horizon (topsoil) | Leaching (removal) of materials in solution
and suspension Maximum accumulation of organic matter |
|
| B - middle horizon (subsoil) | Enrichment in clay, iron, aluminum, organic
matter, sodium Change in colour or structure from horizons above or below |
|
| C - parent material | Unaffected by soil forming processes except for gleying and the accumulation of carbonates and soluble salts | |
| AB, BC, and AC | transitional horizons | |
| Lower case suffixes used to further describe mineral horizons | |
| h | horizon enriched with organic matter (eg. Ah, Ahe, Bh, Bhf) |
| e | eluviated (leached) horizon of clay, iron, aluminum, organic matter (eg. Ae, Ahe) |
| p | plow layer; disturbance by man's activities, such as cultivation (Ap) |
| b | buried horizon (Ab) |
| m | modified by hydrolysis, oxidation or solution to give a change in colour or structure (Bm, Bmk) |
| t | horizon enriched with clay at least 5 cm (2 in.) thick (Bt, Btg, Bnt) |
| n | high Na (sodium) horizon - ration of exchangeable Ca to
Na is 10 or less Prismatic or columnar structure that is hard to very hard when dry (Bn, Bnt) |
| g | grey colours or mottles, indicative of permanent or periodic intense reduction (wet conditions) (Bg, Bgj, Ckg, Ckgj) |
| f | enrichment with non-crystalline Fe and Al combined with organic matter (Bf, Bfh) |
| j | weak (juvenile) expression of soil processes (Btj, Ckgj) |
| k | presence of carbonates, visible by effervescence when dilute HCl is added (Bmk, Ck) |
| ca | layer of carbonate accumulation that exceeds the amount present in the parent material (Cca) |
| s | soluble salts present (Cks) |
| z | frozen horizon (permafrost) |
Soils in Canada are classified using The Canadian System of
Soil Classification, by Agriculture and Agri-Food Canada. This
classification system is similar to the hierarchical classification
system used to classify the plant and animal kingdoms. The system
goes from very broad to very detailed classifications:
Table 1.6 Classification criteria of soils vs. automobiles
| Classification Catergory | Soils | Automobiles |
| I. Order | Chernozemic | General Motors |
| II. Great Group | Black | Car |
| III. Subgroup | Orthic Black | Chevrolet |
| IV. Association | Fine loamy, mixed, cool, subhumid | 4-door Sedan |
| V. Series | Newdale | Impala |
| VI. Phase | NDL/xcxs | loaded, good condition |
| I. Soil Orders - based
on properties that reflect the effects of the
dominant soil-forming processes. |
|
| Chernozemic – | most grassland, agricultural soils in Manitoba (high organic matter in A horizon) |
| Gleysolic – | poorly drained soils (saturated, reduced, mottles) |
| Luvisolic – | forest soils (Ae and Bt horizons) |
| Regosolic – | young soils along rivers, slopes, sand dune areas (weak horizon development) |
| Solonetzic – | sodium-affected soils (sodium in B horizon) |
| Vertisolic – | heavy clay soils with high shrink-swell potential (cracks and shear planes) |
| Brunisolic – | catch-all category (weak B horizon) |
| Cryosolic – | frozen soils |
| Podzolic – | B horizon with Fe, Al, organic matter |
| Organic – | more than 30% organic matter by weight |
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| Figure 1.7 Relative abundance of soil orders found in agro-Manitoba | Figure 1.8 Mineral soil orders
found in agro-Manitoba: 1. Chernozem 2. Luvisol 3. Gleysol 4. Regosol |
Table 1.7 Comparison of four mineral
soils in Manitoba
| Factor | Chernozem | Luvisol | Gleysol | Regosol |
| Native vegetation | Grassland | Forest | Moisture-loving grasses | Limited vegetative growth |
| Moisture regime | Normal | Normal | Wet | Variable to dry |
| Formative processes | Vegetation puts bulk of biomass production below ground | Vegetation puts bulk of biomass production above ground | Moist or saturated conditions affect decomposition process | Relatively young soils not fully stabilized by vegetation |
| Distinguishing features | Thick topsoil horizon (Ah) | Strongly leached horizon (Ae) | Dull, blue-grey colours and mottles (Bg or Cg) | Little soil profile development due to droughtness, erosion, or deposition |
| Typical landscape position | Midslope | Upper slopes | Depressions | Upper slopes |
II. Great Group – broad separations of soil zones based on climate and native vegetation patterns. The five soil zones recognized across the prairies are: Brown, Dark Brown, Black, Dark Grey Chernozems; and Grey Luvisol (Figure 1.9). Climate and vegetation have determined the organic matter levels in the topsoil over time, resulting in darker colours with increasing organic matter content in cooler, wetter regions.
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| Figure 1.9 Soil zones of the Canadian prairies (courtesy PFRA). Scale is 1 inch = 230 miles (1:14,572,800) |
III. Subgroup – subdivisions of each great group. For the Chernozem great group, the subgroups are:
IV. Soil Association (or Catena) - a sequence or family of related soils located in the same climatic zone formed from similar parent material under different landscape positions resulting in different profile characteristics. These soils are adjacent to one another from hilltop to depression. Variation in soil horizons from hilltop to depression is caused by the amount of water available at each point along the slope as a function of infiltration, runoff, run-on and proximity to the water table. Each soil type located along the slope is a soil series (e.g. The Newdale association includes six soil series: Newdale, Rufford, Varcoe, Angusville, Penrith and Drokan).
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Figure 1.10 Soils of the Newdale Association |
V. Soil Series - an individual soil type, with a particular kind and arrangement of soil horizons developed on a particular type of parent material and located in a particular soil zone. The properties of a particular soil series are determined by moisture influences and landscape position. As a result, an individual soil series can usually be found in a specific part of a given field.
A soil series name is often derived from a town or landmark in or near the area where the series was first recognized (e.g. Newdale soil series).
VI. Soil Phases - variations of a soil series because of factors such as erosion, topography (slope), stones, salinity, improved drainage and peaty layers. This type of information is only found in detailed soil survey reports.
*Sensitive crops may exhibit negative effects of salinity at levels <4 dS/m - this is a general salinity rating for traditional annual crops (wheat, canola) which are not significantly affected by soil salinity levels below 4 dS/m.
Other rating systems (refer to Manual for Describing Soils in the Field) evaluate salinity with greater detail using the following classes:
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