Building Soils for Better Crops Sustainable Soil Management by Fred Magdoff and Harold Van Es - HTML preview

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Chapter 5

soil PartiCles, Water, and air

Moisture, warmth, and aeration; soil texture; soil fitness; soil organisms; its tillage, drainage, and irrigation; all these are quite as important factors in the make up and maintenance of the fertility of the soil as are manures, fertilizers, and soil amendments.

—J.l. hills, C.h. Jones, and C. Cutler, 1908

The physical condition of a soil has a lot to do with

clay, clay loam, loam, sandy loam, or sand—is perhaps

its ability to produce crops. A degraded soil usually has

its most fundamental inherent characteristic, as it

reduced water infiltration and percolation (drainage into

affects many of the important physical, biological, and

the subsoil), aeration, and root growth. These conditions

chemical processes in a soil and changes little over time.

reduce the ability of the soil to supply nutrients, render

harmless many hazardous compounds (such as pesti-

cides), and maintain a wide diversity of soil organisms.

organic matter

Small changes in a soil’s physical conditions can have

soil wets up

during rain

a large impact on these essential processes. Creating a

air

good physical environment, which is a critical part of

soil dries down

building and maintaining healthy soils, requires atten-

tion and care.

mineral

matter

Let’s first consider the physical nature of a typical

water

mineral soil. It usually contains about 50% solid par-

ticles and 50% pores on a volume basis (figure 5.1). We

discussed earlier how organic matter is only a small, but

a very important, component of the soil. The rest of a

solids

pores

soil’s particles are a mixture of variously sized minerals

that define its texture. A soil’s textural class—such as a

Figure 5.1. Distribution of solids and pores in soil.

Photo courtesy Ray Weil

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chAPter 5 soil PartiCles, Water, and air

least—they’re visible) and no aggregation due to a lack

100

of organic matter or clay to help bind the sand grains.

10

90

A good loam or clay soil, on the other hand, has smaller

20

particles, but they tend to be aggregated into crumbs

80

30

per

that have larger pores between them and small pores

ay 70

clay

cent silt

40

within. Although soil texture doesn’t change over time,

cent cl 60

50

the total amount of pore space and the relative amount

per 50

silty

60

of variously sized pores are strongly affected by man-

sandy

clay

40

clay

silty clay

agement practices—aggregation and structure may be

clay loam

loam

70

30

destroyed or improved.

sandy clay loam

80

20

sandy loam

loam

silt loam

90

10

WATER AND AERATION

loamy

silt

sand sand

100

Soil pore space can be filled with either water or air, and

100

90

80

7

60

0

50

40

30

20

10

their relative amounts change as the soil wets and dries

percent sand

(figures 5.1, 5.3). When all pores are filled with water,

the soil is saturated, and the exchange of soil gases with

Figure 5.2. The percentages of sand, silt, and clay in the soil textural

atmospheric gases is very slow. During these conditions,

classes. From USDA-NRCS.

carbon dioxide produced by respiring roots and soil

The textural class (figure 5.2) is defined by the relative

organisms can’t escape from the soil and atmospheric

amounts of sand (0.05 to 2 mm particle size), silt (0.002

oxygen can’t enter, leading to undesirable anaerobic (no

to 0.05 mm), and clay (less than 0.002 mm). Particles

oxygen) conditions. On the other extreme, a soil with

that are larger than 2 mm are rock fragments (pebbles,

little water may have good gas exchange but be unable to

cobbles, stones, and boulders), which are not considered

supply sufficient water to plants and soil organisms.

in the textural class because they are relatively inert.

Water in soil is mostly affected by two opposing

Soil particles are the building blocks of the soil skel-

forces that basically perform a tug of war: Gravity pulls

eton. But the spaces (pores) between the particles and

water down and makes it flow to deeper layers, but

between aggregates are just as important as the sizes of

water also has a tendency to stay in a soil pore because

the particles themselves. The total amount of pore space

it is attracted to a solid surface and has a strong affin-

and the relative quantity of variously sized pores—large,

ity for other water molecules. The latter are the same

medium, small, and very small—govern the important

forces that keep water drops adhering to glass surfaces,

processes of water and air movement. Soil organisms

live and function in pores, which is also where plant

roots grow. Most pores in clay are small (generally less

than 0.002 mm), whereas most pores in sandy soil are

large (but generally still smaller than 2 mm).

Figure 5.3. A moist sand with

pores between grains that

The pore sizes are affected not only by the relative

contain water and air. The

amounts of sand, silt, and clay in a soil, but also by the

larger pores have partial y

drained and al owed air entry,

amount of aggregation. On the one extreme, we see that

while the narrower ones are

beach sands have large particles (in relative terms, at

still filled with water.

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chAPter 5 soil PartiCles, Water, and air

as gravitational drainage (figure

wilting point

field capacity

5.4b). In this case, the soil has more

plant-available water than a coarse

unavailable

plant-

a) sand

available

gravitational water

sand, but plants will suffer from long

water

water

periods of poor aeration following

b) dense clay

plant-

unavailable

saturating rains.

available

water

water

These different effects of vari-

c) aggregated loam

gravitational

ous pore sizes have great impacts:

unavailable

water

water

plant-available water

Leaching of pesticides and nitrates

to groundwater is controlled by the

0

soil water content

saturation

relative amounts of different sizes

of pores. The rapidly draining sands

Figure 5.4. Water storage for three soils.

may more readily lose these chemi-

cals in the percolating water, but this

and their effect is stronger in small pores (figure 5.3)

is much less of a problem with fine loams and clays.

because of the closer contact with solids. Soils are a

For the latter, the more common anaerobic conditions

lot like sponges in the way they hold and release water

resulting from extended saturated conditions cause

(figure 5.4). When a sponge is fully saturated, it quickly

other problems, like gaseous nitrogen losses through

loses water by gravity but will stop dripping after about

denitrification, as we will discuss in chapter 19.

30 seconds. The largest pores drain rapidly because they

The ideal soil is somewhere between the two

are unable to retain water against the force of gravity.

But when it stops dripping, the sponge still contains a

large pore

small pore

lot of water, which would, of course, come out if you

intermediate

pore

squeezed it. The remaining water is in the smaller pores,

which hold it more tightly. The sponge’s condition

following free drainage is akin to a soil reaching field

capacity water content, which in the field occurs after

about two days of free drainage following saturation by

a lot of rain or irrigation. If a soil contains mainly large

pores, like a coarse sand, it loses a lot of water through

quick gravitational drainage. This drainage is good

because the pores are now open for air exchange. On

the other hand, little water remains for plants to use,

resulting in more frequent periods of drought stress.

Coarse sandy soils have very small amounts of water

aggregate (crumb)

available to plants before they reach their wilting point

(figure 5.4a). On the other hand, a dense, fine-textured

Figure 5.5. A well-aggregated soil has a range of pore sizes. This medium-soil, such as a compacted clay loam, has mainly small

size soil crumb is made up of many smal er ones. Very large pores occur

pores, which tightly retain water and don’t release it

between the medium-size aggregates.

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chAPter 5 soil PartiCles, Water, and air

Figure 5.6. Left: Corn root in a compacted soil cannot access water and nutrients from most of the soil volume. Right: Dense rooting al ows for full exploration of soil water and nutrients.

extremes, and its behavior is typical of that exhibited by

not obtain the moisture it needed. The corn roots on

a well-aggregated loam soil (figures 5.4c, 5.5). Such a

the right (figure 5.6) were able to fully explore the soil

soil has a sufficient amount of large pore spaces between

volume with many roots, fine laterals, and root hairs,

the aggregates to provide adequate drainage and aera-

allowing for better water and nutrient uptake.

tion during wet periods, but also has enough small pores

Similarly, the depth of rooting can be limited by

and water-holding capacity to provide water to plants

compaction. Figure 5.7 shows, on the right, corn roots

and soil organisms between rainfall or irrigation events.

from moldboard-plowed soil with a severe plow pan.

Besides retaining and releasing water at near optimum

The roots could not penetrate into the subsoil and were

quantities, such soils also allow for good water infiltra-

therefore limited to water and nutrients in the plow

tion, thereby increasing plant water availability and

layer. The corn on the left was grown in soil that had

reducing runoff and erosion. This ideal soil condition is

been subsoiled, and the roots were able to reach about

therefore characterized by crumb-like aggregates, which

twice the depth. Subsoiling opened up more soil for

are common in good topsoil.

AVAIlAblE WATER AND ROOTINg

There is an additional dimension to plant-available

water capacity of soils: The water in the soil may be

available, but roots also need to be able to access

it, along with the nutrients contained in the water.

Consider the soil from the compacted surface horizon in

figure 5.6 (left), which was penetrated only by a single

corn root with few fine lateral rootlets. The soil volume

held sufficient water, which was in principle available

to the corn plant, but the roots were unable to penetrate

Figure 5.7. Corn roots on the right were limited to the plow layer due to a severe compaction pan. Roots on the left penetrated into deeper soil

most of the hard soil. The corn plant, therefore, could

following subsoiling and could access more water and nutrients.

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chAPter 5 soil PartiCles, Water, and air

root growth and, therefore, more usable

water and nutrients. Thus, plant water

precipitation

availability is a result of both the soil’s

water retention capacity (related to tex-

ture, aggregation, and organic matter)

evapo-transpiration

and potential rooting volume, which is

infiltration

influenced by compaction.

runoff

soil water storage

INFIlTRATION VS. RUNOFF

An important function of soil is to absorb

water at the land surface, and either store

percolation

it for use by plants or slowly release it

to groundwater through gravitational

to stream

flow (figure 5.8). When rainfall hits the

to deep

stream

groundwater

ground, most water will infiltrate the soil;

but some may run off the surface, and

Figure 5.8. The fate of precipitation at the land surface determines whether water infiltrates or some may stand in ruts or depressions

runs off the surface.

before infiltrating or evaporating. The

maximum amount of rainwater that can enter a soil in a

as pores are blocked with ice. Runoff happens more

given time, called infiltration capacity, is influenced by

readily with poorly managed soils, because they lack

the soil type, structure, and moisture content at the start

strong aggregates that hold together against the force

of the rain.

of raindrops and moving water and, therefore, have few

Early in a storm, water usually enters a soil readily,

large pores open to the surface to quickly conduct water

as it is literally sucked into the dry ground. As the soil

downward. Such runoff can initiate erosion, with losses

wets up during a continuing intense storm, water entry

of nutrients and agrochemicals as well as sediment.

into the soil is reduced and a portion of rainfall begins

to run downhill over the surface to a nearby stream or

SOIl WATER AND AggREgATION

wetland. The ability of a soil to maintain high infiltra-

Processes like erosion, soil settling, and compaction are

tion rates, even when saturated, is related to the sizes

affected by soil moisture conditions, and in turn affect

of its pores. Since sandy and gravelly soils have more

soil hardness and the stability of aggregates. When soil

large pores than do fine loams and clays, they maintain

is saturated and all pores are filled with water, the soil is

better infiltration during a storm. But soil texture is also

very soft. (Fungal hyphae and small roots also serve to

important in governing the number of pores and their

form and stabilize aggregates deeper in the soil.) Under

sizes: When finer-textured soils have strong aggregates

these saturated conditions, the weaker aggregates may

due to good management, they can also maintain high

easily fall apart from the impact of raindrops and allow

infiltration rates.

the force of water moving over the surface to carry soil

When rainfall exceeds a soil’s infiltration capac-

particles away (figure 5.9). Supersaturated soil has no

ity, runoff is produced. Rainfall or snowmelt on frozen

internal strength, and the positive water pressure in fact

ground generally poses even greater runoff concerns,

pushes particles apart (figure 5.10, left). This makes soil

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chAPter 5 soil PartiCles, Water, and air

and susceptible to wind erosion (figure 5.10, right).

Strong aggregation is especially important during

these moisture extremes, as it provides another source

of cohesion that keeps the soil together. Good aggrega-

tion, or structure, helps to ensure a high-quality soil and

prevents dispersion (figure 5.11). A well-aggregated soil

also results in good soil tilth, implying that it forms a

good seedbed after soil preparation. Aggregation in the

surface soil is enhanced by surface residue and lack of

tillage. Also, a continuous supply of organic materials,

roots of living plants, and mycorrhizal fungi hyphae are

needed to maintain good soil aggregation.