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| Soil
Management: The Soil Resource
| Author: | OMAFRA Staff
| | Creation Date: | 4
May 2009 | | Last Reviewed: |
4 May 2009 |
|
Corn | Soybeans
| Forages | Cereals
| Dry Edible Beans | | Spring
and Winter Canola | Other Crops
| Soil Management | | Soil
Fertility and Nutrient Use | Field
Scouting | | On-Farm Stored
Grain Management | Weed Control
| | Insects and Pests of Field
Crops | Diseases of Field Crops
| Appendices | Pub
811: Agronomy Guide > Soil Management
> The Soil Resource Excerpt from Agronomy Guide for Field
Crops Order OMAFRA Publication
811: Agronomy Guide for Field Crops Soil Formation The
properties of Ontario's soils are related closely to landforms that were created
by glacial ice, meltwaters, glacial lakes and wind. Glaciers moved across all
of Ontario grinding rock into fine particles, and mixed and moved existing soil.
As the glaciers retreated, they dropped soil materials from within the ice itself.
The meltwater deposited gravel and sands as mixed layers. Flat beds of sand, silt
and clay were deposited by lakes that formed from the ponding of melt waters.
The soils were further distributed as strong winds moved across these landscapes.
The soils of today were developed on these deposits. Examples of the
landforms include shallow-over-bedrock, muck or peat, till plain, end moraine,
sand plain and clay plain. Additional information and photo examples of the landforms
can be found in Best Management Practices: Soil Management, Order No. BMP06E.
See also the Soil Management page on the OMAFRA website at www.ontario.ca/crops. Soil
Variability The soils of Ontario vary greatly in their make-up due to
the scraping and mixing action of glacier movement. As the glaciers melted, wind,
water and time contributed to further differences in soil development. Some soils
are very shallow to bedrock, others have more than 100 m (328 ft) of overburden.
The depth of topsoil varies as conditions for soil formation varied. Soils vary
from region to region, from farm to farm and within fields. Observe a soil excavation
to see the variation in the depth of soil horizons (shown in Figure
8-1, Variability in Soil Horizons). This natural variation often occurs
over very short distances. Growers have been aware of this soil variability
for years and have tried to improve areas that were less productive. Figure
8-1. Variaibility in Soil Horizons

Yield monitors have allowed us to see how much that variability can
affect yields. In some fields of corn, there can be an over-6.3 t/ha (100 bu/acre)
difference between high- and low-yielding areas. Soybeans can have a 2.7 t/ha
(40 bu/acre) spread and wheat a spread of up to 5.4 t/ha (80 bu/acre).
Soils can vary in: - mineral composition, texture, fertility, pH
- soil
organic matter: amount and type
- structure, aeration, drainage, density,
water-holding capacity
- thickness of horizons, topographic position
- age:
degree of weathering, erosion, deposition
- depth to:
- bedrock
- water
table
- textural or structural changes
Intensive crop production has contributed to the variation in topsoil depth. Soil
erosion by wind, water and tillage has reduced the amount of topsoil in parts
of many fields. That topsoil, in some cases, is deposited in other areas of the
field, increasing topsoil depth there, while in some fields, the topsoil has been
lost totally from areas. Other examples of management that can intensify variability
include liming, removal of fence rows, compost/manure piles and uneven manure
application patterns. Table
8-1. Soil Organic Matter Pools |
Property | Active
Soil Organic Matter (living) | Moderately
Stable (dead) | Very Stable
(very dead) | | Activity | - living or recently
deceased
- living part includes bacteria, fungi, algae, plant roots, insects,
earthworms, etc., which help with the breakdown of residues and manures
- supplies
nutrients as well as glues for aggregate formation
- recently dead includes
dead organisms, recently added manures, old plant roots and crop residues
- supplies
food for organisms
| - recently decomposed organic
material
| - sometimes called humus
- virtually
untouchable, intimate part of the soil
- holds on to some nutrients for
slow release
- can lessen drainage or compaction problems
- can improve
water retention in sandy soils
| | Persistence |
- influenced by year-to-year management
| - influenced
over a farmer's lifetime
| - existed long before the field
was farmed and will exist long after the farmer retires
|
| Percentage of soil organic matter | 10%-15% | 40%-45% | 40%-45% |
What Is Good Quality Soil? Soil quality is the measure of
a soil's health and its ability to resist erosion, compaction and other stresses,
while maintaining economic productivity. Many factors are assessed to determine
a soil's health. A healthy soil will: - have good soil structure, resist
crusting and have minimal compaction
- have an abundance of earthworms
- have
a fresh, earthy odour
- readily decompose residue
- have good drainage,
water movement and water-holding capacity
- encourage seedling emergence
and root growth
- produce uniform crop growth and colour
- have nutrient
levels, pH and organic matter in the optimal range
- have suffered little
wind, water or tillage erosion, and will be resistant to it
Most of
the characteristics of a healthy soil have a direct or indirect link to soil organic
matter. Organic Matter Soil organic
matter is a very small component of the soil but it plays a crucial role. Building
and maintaining good levels of soil organic matter results in:
- higher-yielding,
healthier crops
- crops more tolerant to doughty conditions and other stresses,
such as insects and diseases
- a reduced need for commercial fertilizer
and lime
Soil organic matter exists in three pools in the soil. See
Table 8-1, Soil Organic Matter Pools. Importance
of Organic Matter (OM) Crucial to many aspects of the soil and crop development
and with no single role taking precedence, organic matter: - directly
or indirectly influences the availability of nutrients obtained from the soil,
playing an important role in many nutrient cycles
- improves the cation
exchange capacity (CEC) of a soil by helping the soil hold on to positively charged
ions such as calcium, potassium and magnesium making them available to the crop.
This is most important in loams and sands, where there is little clay to provide
the negative charge to hold the cations.
- forms complex organic acids during
the breakdown of organic materials, which also hold on to nutrients, and helps
keep iron, zinc and manganese in the chelated or available form
- can buffer
soil pH, slowing rapid changes in pH
- darkens soil colour, helping warm
the soil faster in the spring
- helps store carbon - there is four times
as much C in the soil as in plants
- stores nitrogen - almost all the nitrogen
in soils exists as part of the organic matter. Bacteria and fungi convert the
organic format to nitrate and ammonium, which can be used by plants.
- maintains
the water cycle by keeping the soil open and porous, so more water can soak into
the soil. Infiltration, rather than runoff, replenishes soil moisture during dry
conditions and contributes to recharge of groundwater. This in turn increases
the amount of water that plants can access from the soil, by increasing both storage
capacity and rooting volume, and improves drainage of excess water through the
soil.
- aerates the soil, creating greater porosity so air can enter the
soil more easily
There is also some evidence that organic matter may
help prevent phosphorus from being converted to forms that are unavailable to
plants. Soil Life A healthy soil is full
of life. The organisms living in the soil play an important role in the health
of the soil and of plants. Soil life includes bacteria, fungi, algae, protozoa,
nematodes, earthworms, insects (ants, beetles, millipedes, etc.), larger animals
(moles, rabbits, snakes, etc.) and plant roots. Soil organisms play an
important role: - in the breakdown of organic residues and their incorporation
into the soil. As organic materials are decomposed, nutrients become available
to plants, humus is produced and soil aggregates are formed.
- creating
channels for water infiltration and better aeration
- in moving surface
residues deeper into the soil
- in nitrogen fixation
- in fighting
plant pests, such as weeds, insects, nematodes and diseases
- stimulating
root growth with substances produced by microorganisms
Soil StructureThe
term soil tilth is used to describe a soil that is in a favourable condition for
crop growth. Soil with good tilth is porous and allows water to enter easily,
instead of running off the surface, which makes it more available to plants and
results in less erosion. A porous soil allows roots to exchange oxygen and eliminate
carbon dioxide more easily, which aids root growth. Soils and soil structure
are formed through the actions of freeze-thaw cycles, wet-dry cycles, root growth,
tillage, and soil animals and microorganisms. The active organic matter
in a soil, the decomposing residues and the soil life play a significant role
in soil structure development and maintenance. Soil structure is developed from
soil particles held together with clay, humus and the glues released from living
and decomposing organisms. Good soil aggregation or structure can only be maintained
with a continuous supply of organic materials, roots of living plants and soil
organisms. Table 8-2, Types of Soil Structure,
describes soil structure typically seen in soils. Soil CompactionCompaction
is defined as increased bulk density and reduction in soil pore space. This occurs
when the soil particles are forced closer together by the impact of equipment,
animals and raindrops. The use of heavier tractors, combines and implements, particularly
with earlier spring tillage, can cause problems under any tillage system.
A soil that is in poor tilth has structure that has deteriorated and aggregates
that are not stable. This can be seen as increased compaction, decreased aeration
and a reduction in water storage. Heavy equipment travelling across the soil can
cause significant soil compaction. This can have a negative impact on the soil
biology. The reduction in the number of medium to large pores reduces the volume
of soil available for air, water and populations of organisms that require large
spaces in which to live. There are three types of soil compaction that can be
found in the soil: surface crusting, tillage layer compaction and subsoil compaction.
See Table 8-3, Types of Soil Compaction, for a
description of each. Soils having high organic matter contents, good
internal drainage and good structure are less susceptible to compaction. For further
information, see the OMAFRA website at www.ontario.ca/crops. Threat
to the Resource The biggest threats to the soil resource are the loss
of soil organic matter, the lack of a thriving and diverse population of organisms,
and soil compaction. As agriculture has become more mechanized and many
rotations have become shorter and more intense, the quality of many soils in Ontario
has declined over the last 4 to 5 decades. The soil is vulnerable to degradation.
Soils that are degraded are usually the result of soil erosion and a decline in
organic matter levels. Soils in this state often end up on a downward spiral.
Further loss of topsoil due to erosion reduces the nutrient content of the soil.
The lost soil carries nutrients with it so the topsoil layer becomes less fertile.
Tillage of the soil begins to incorporate less fertile soil from below. As organic
matter levels decline, the soil becomes less resistant to erosion. The soil also
becomes less resistant to soil compaction. As compaction increases, porosity is
reduced and there is less air and less water movement through the soil. More runoff
causes more erosion. As organic matter levels decline, the soil has less water-holding
capacity. The cycle continues in a downward spiral of soil degradation. Soil
Erosion Soil erosion is a serious threat to the productivity of the
soil. Soil erosion is a naturally occurring process, but farming practices have
accelerated the rates of erosion. Erosion in agricultural fields involves the
detachment and movement of soil particles within and outside the field. It results
in:
- decreased crop yields
- increased cost of production
- degraded
topsoil
- increased runoff and reduced water storage
Table
8-3. Types of Soil Compaction | Cause |
Impact | | Surface
crusting | - Unprotected soil is dispersed by
the action of raindrops and pushed into a thin, dense surface layer.
|
- Soil is prone to high rates of runoff and water erosion.
- The
surface becomes sealed, reducing water infiltration.
- When dry, a hard
crust forms, which can delay or prevent seedling emergence.
|
| Tillage layer compaction |
- Soil is eroded.
- Soil has low levels of organic matter.
- Heavy
field equipment traffic results in soil compaction.
|
- The layer is very dense, reducing water infiltration and the porosity of the
soil.
- Root growth may be restricted.
| | Subsoil
compaction | - Pressure from a disc or plow
on the soil below the tillage layer compacts the subsoil.
- Pressure from
heavy field equipment with poor weight distribution results in compaction.
| - Water flow is restricted through the compacted layer.
- There
will be little or no root growth through the compacted layer.
|
The three types of soil erosion are water, wind and tillage. Water
erosion is the detachment and movement of unprotected soil particles by water.
Wind erosion is the detachment and movement of soil particles by air currents
or wind. Tillage erosion occurs when tillage equipment lifts soil and moves it
forward, gravity pulls it downhill. See the booklets Best
Management Practices: Soil Management, Order No. BMP06E, and Best
Management Practices: Field Crop Production, Order No. BMP02E, for more
information. For more information:
Toll Free: 1-877-424-1300
Local: (519) 826-4047
E-mail: ag.info.omafra@ontario.ca
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