Soil Fertility, Degradation, and Conservation
1. What is Fertility?
Imagine two soils. One is chernozem—dark, granular, with the smell of earth after rain. The other is barren sand—gray and loose, where nothing grows. What is the fundamental difference between them? Why does one give life to plants and the other does not? The answer lies in a fundamental property that distinguishes soil from any rock: fertility.
Fertility is the reason we study soil as agronomists. It is not an abstract concept but a concrete ability of the soil to provide plants with everything they need. Today, our task is to understand precisely what lies behind this concept, how it has been shaped, and why the modern understanding of fertility extends far beyond just a "set of nutrients."
Historical Development of the Concept: From Dokuchaev to the Present
The understanding of fertility has undergone a long evolution. Let's trace the main milestones.
1. Pre-scientific Period: Empirical Agriculture
For millennia, farmers knew that some lands were "good" and others "bad." They applied manure, ash, left fields fallow, but had no scientific explanation for why it worked. Fertility was perceived as a given, mysterious property of the land.
2. V.V. Dokuchaev: Fertility as a Consequence of Soil Formation
In the late 19th century, the great Russian scientist Vasily Vasilyevich Dokuchaev revolutionized earth science. He proved that soil is an independent natural body, formed through the complex interaction of five factors: parent material, climate, topography, living organisms, and time. Dokuchaev showed that fertility is not an innate quality of the rock, but the result of a long-term soil-forming process. It is in this process that organic matter, nutrients, and a favorable structure accumulate in the upper layers of rocks.
"Since all the most important soil-formers are distributed on the earth's surface in the form of belts or zones... it is inevitable that soils should also be distributed zonally" (V.V. Dokuchaev, cited in Mukha et al., 2003, p. 196).
This concept of soil zonality laid the foundation for understanding why the fertility of different soils naturally differs.
3. Fertility as "Capability": From Statics to Dynamics
In the 20th century, a classical definition emerged, which we find in fundamental works: "Soil fertility is the status of the soil with respect to its ability to supply the elements essential for plant growth without toxic concentration of any element" (Foth & Ellis, 1997, p. 1).
Note the key points of this definition, which are still relevant today:
- Ability to supply—that is, not just to contain, but to give.
- Essential elements—a balanced set of macro- and micronutrients.
- Without toxic concentration—fertility implies not only sufficiency but also the absence of harmful substances.
However, this definition, for all its precision, did not reflect the full complexity of the phenomenon. Further scientific development showed that fertility cannot be reduced to chemistry alone.
4. V.R. Williams and the "Law of Return": The Agronomic View
V.R. Williams, the creator of the grassland farming system doctrine, emphasized the inextricable link between fertility and biological processes. He focused on the role of perennial grasses and structural aggregates. His ideas on the necessity of returning nutrients to the soil formed the basis of the law of return—one of the fundamental laws of agriculture, which states that to maintain fertility, it is necessary to compensate for the removal of nutrients with the harvest (Mukha et al., 2003, p. 191).
5. Modern Systems Approach: Fertility as an Integrative Function
Today, we view fertility much more broadly. It is not just a "box of fertilizers" but an integrative property of the soil as an ecosystem. In the modern understanding, fertility is the ability of the soil, as a component of the biosphere, to provide the terrestrial factors and conditions necessary for plant life, determining the nutrient, water-air, thermal, redox, and other regimes (Mukha et al., 2003, p. 184).
The key point here is the ecosystem approach. We are moving from understanding soil as a passive substrate to understanding it as an active, living system, where properties and regimes (not only chemical but also physical and biological) are in constant interaction.
Why is Fertility a Property of Soil, Not Plants?
This question is crucial for delineating our subject—soil science—from agrochemistry and plant physiology.
Fertility is potential, not result.
Let's recall the classic image: soil is a "storehouse", and plants are "consumers". Fertility is a characteristic of the storehouse itself: its size, fullness, preservation, and ease of access. Plants, using this potential, create a yield.
In soil science, the concepts of "potential" and "effective" fertility are used for this (Foth & Ellis, 1997).
- Potential fertility—is the natural reserve accumulated in the soil over a long period of soil formation. It is determined by the reserves of humus, nutrients, and the physical properties of the soil. It is like the soil's capital.
- Effective fertility—is the degree to which this potential is used by plants under specific conditions. It depends not only on the soil but also on technology, weather, and the plant itself. It is like the income from the capital.
Valkov et al. (2004) emphasize that fertility is "the ability to ensure plant growth and productivity," but not productivity itself. A soil can be fertile, but the yield on it can be low due to drought, poor agricultural practices, or an incorrectly chosen variety. Conversely, a high yield can be obtained on less fertile soil by applying intensive technologies. But this will be the result of high artificial fertility, not a natural property of the soil.
"Artificial fertility cannot exist separately: combining with natural fertility, it forms a qualitatively new category—natural-economic (natural-anthropogenic) fertility" (Mukha et al., 2003, p. 185).
Therefore, when discussing fertility, we are always talking about a property of the soil, about its internal organization and potential. Plants, on the other hand, are tools that allow us to assess the effectiveness of this potential, but they are not its source.
What Constitutes Fertility? Integration of Knowledge
Fertility is a systemic property that arises from the interaction of four groups of factors, corresponding to sections of previously studied modules. To understand fertility, we need to recall everything we know about soil. Simply put, fertility is a balanced combination of:
1. Physical Basis (Module "Soil Physics"):
- Particle size distribution (the ratio of sand, silt, and clay)—determines the water-air regime and absorption capacity.
- Structure—the ability of soil to form aggregates. It is structure that ensures the optimal ratio of solid, liquid, and gaseous phases. As E.V. Shein wrote (cited in Weil & Brady, 2017), structure is the "skeleton" of soil fertility.
- Density and porosity—determine the availability of oxygen for roots and microorganisms, as well as water permeability.
2. Water and Air Regimes (Modules "Water" and "Air"):
- Water—the main solvent and transport medium for nutrients. Fertility is impossible without sufficient, but not excessive, moisture (Scheffer et al., 2018).
- Air—plant roots and aerobic microorganisms need oxygen for respiration. Soil fertility is closely linked to its aeration.
3. Chemical Basis (Modules "Chemical Properties" and "Organic Matter"):
- Humus content—is the heart of fertility. Humus is not just "dead" organic matter but a complex complex that determines the absorption capacity, buffering capacity, nutrient reserve (primarily nitrogen), and water-physical properties (Baldock, 2012).
- Reaction of the environment (pH)—affects the availability of all nutrients. In too acidic or alkaline conditions, even a rich soil can be infertile for many crops (Weil & Brady, 2017).
- Reserves of available elements—macro- (N, P, K, Ca, Mg, S) and micronutrients (Fe, Zn, Cu, Mn, etc.).
4. Biological Activity (Module "Soil Biota"):
- Microorganisms—the main "processors" of organic matter. They mineralize humus, converting elements into forms available to plants. Without them, the cycle of substances in the soil would be impossible (Huang, 2012).
- Soil fauna (worms, insects, etc.)—create macropores, improve aeration, and mix soil layers.
All these components do not exist in isolation. They form a unified system. For example, poor structure (physics) worsens the water-air regime, which, in turn, reduces microbiological activity (biology) and slows down the release of nutrients from humus (chemistry). This is precisely why fertility is an integrative characteristic of the soil, not a sum of individual properties.
Fertility as a Dynamic Characteristic: Soil—a Renewable but Limited Resource
From our discussion follows a crucial conclusion: fertility is not a constant value. It is a dynamic property that can either increase (as a result of cultivation) or decrease (as a result of degradation).
"Soil fertility is characterized by high dynamism and clearly responds to changes in the factors and conditions of soil formation" (Mukha et al., 2003, p. 184).
Soil is, in a sense, a renewable resource. We can restore its fertility by applying fertilizers, adding organic matter, and using proper crop rotations. Nature is also capable of self-recovery, but this takes centuries.
However, despite its potential renewability, soil is a limited and extremely vulnerable resource:
- Recovery time. The formation of one centimeter of fertile topsoil can take from 100 to 400 years (Troeh & Thompson, 1993). The loss of this layer due to erosion can occur in a single season.
- Irreversibility of some losses. The disappearance of humus, destruction of structure, and loss of soil organisms are processes that are either irreversible or require enormous costs for restoration.
- Limited area. The area of soils suitable for agriculture on the planet is finite and is constantly shrinking due to urbanization, erosion, and degradation (Brady & Weil, 2017).
Understanding this paradox—the dynamism and simultaneous vulnerability of fertility—has led to the formation of the concept of sustainable soil management.
This concludes the first chapter of our lecture. We have examined how the understanding of fertility has changed, why it is a property of the soil and not of plants, and what components form it. This is the foundation upon which we will build further discussion. In the second chapter, we will move on to how this knowledge is applied in practice within the framework of sustainable soil management.
2. Why is Fertility a Property of Soil, Not Plants?
Distinguishing Concepts: A Fundamental Question for the Agronomist
In the previous chapter, we established that fertility is the ability of the soil to provide plants with everything they need. But a natural question arises: if plants grow on the soil and produce a yield, could fertility be a property of the plant itself—its ability to effectively use what the soil provides? Or perhaps fertility is the result of the joint work of soil and plant?
These questions are not idle. The answer determines our entire farming system: how we assess land, what technologies we apply, how we build crop rotations, and how we understand degradation. If we answer incorrectly, we will treat the wrong "disease" with the wrong "medicines."
Key thesis of this chapter: fertility is a property of the soil as a natural body. Plants are "users," not "creators" of this property (although they do influence it).
Fertility as an Attribute of the Soil Body
Let us recall V.V. Dokuchaev's fundamental discovery: soil is an independent natural body. Like any natural body, it possesses a set of its own, inherent properties. Fertility is one such property that distinguishes soil from rock (Scheffer et al., 2018).
Fertility is the main specific property of soil, qualitatively distinguishing it from the original (parent) rock
(Mukha et al., 2003, p. 184).
This means that fertility is "built into" the soil; it is an integral characteristic, much like color, density, or porosity. It exists in the soil regardless of whether a plant is growing on it or not.
Take, for example, chernozem lying fallow. There are no cultivated plants on it, yet it remains fertile. Its fertility is a potential, a reserve accumulated over millennia of the sod process. And this potential can be realized as soon as plants appear. Conversely, desert sand remains infertile, even if rare plants temporarily appear on it. Fertility is an immanent property of the soil material itself, not a result of its use.
Potential and Effective Fertility: The Key to Understanding
To definitively distinguish between a soil property and the result of its use, soil science has introduced two key concepts, which we have already mentioned.
Potential fertility (also called natural or inherent)—is "a characteristic of the soil determined by its natural, genetic features and inherent to the soil as a natural body" (Valkov et al., 2004, p. 436). It is assessed by reserves of humus, nutrients, physicochemical properties, structure, etc. This is the soil's capital.
Effective fertility (or actual)—is "the degree of use of these possibilities" (ibid.). It is that part of the potential fertility that is realized in the yield under specific conditions of the year, technology, and variety. This is the income from the capital.
Imagine two chernozems with the same potential. On one, the farmer applies intensive technology, uses fertilizers, and irrigates—and gets a high yield. On the other, the farmer manages extensively, without fertilization—and the yield is low. The potential fertility of these soils is the same, but the effective fertility is different. The reason for the difference lies not in the soil but in how the farmer (and the plants) managed its potential.
Currently, fertility is understood as the ability of the soil, as a component of the biosphere, to provide the terrestrial factors and conditions necessary for plant life... Natural fertility characterizes the initial potential capabilities of the soil, while actual (effective) fertility characterizes the degree of use of these capabilities
(Mukha et al., 2003, p. 185).
Thus, effective fertility is already a result of the interaction of soil, plant, climate, and humans. But its basis, its root, is the potential fertility of the soil itself.
Ecological Specificity of Fertility: A Soil Property, but Not Absolute
Another important argument for fertility being a property of the soil lies in its ecological specificity. The same soil can be fertile for some plants and completely infertile for others. This is a property of the soil, not the plant.
As Pliny the Elder wrote: "The soil that is adorned with tall and stately trees is by no means the best, except for its suitability for the trees themselves" (cited in Valkov et al., 2004, p. 439).
Valkov et al. (2004, p. 438) emphasize: "The main paradox of fertility is that all soils possess fertility, and yet there are no generally fertile lands at all. Their fertility is very specific." Tea and lupine grow only on acidic soils, while alfalfa prefers neutral ones. Heavy structural soils are optimal for grains, while potatoes do better on lighter ones. On soils rich in organic matter, the quality of grapes and tobacco decreases, while hemp and vegetables require precisely such soils.
This diversity of requirements is not a property of plants but a reflection of the diversity of soils. It is precisely because soils have different properties (pH, particle size distribution, humus content, etc.) that they differently match the ecological needs of different plants. Soil fertility is its correspondence to the needs of a specific plant. If we change the plant, we change the assessment of the fertility of the same soil. But the property remains a property of the soil.
Distinction from Agrochemistry and Crop Science
For us agronomists, this distinction has fundamental practical significance.
Agrochemistry studies the transformations and application of fertilizers. Fertilizers are a means of managing fertility, but they are not fertility itself. Fertilizers can increase effective fertility by compensating for the removal of elements, but they do not create fertility "from scratch." As stated in the law of return, we return to the soil what was taken from it. The soil remains the "master" of fertility, and fertilizers are just a tool. Without the soil matrix, its structure, and its buffering capacity, fertilizers would be just a saline solution, incapable of ensuring sustainable growth.
Crop science studies the technologies of cultivating crops. It uses soil fertility, creating optimal conditions for its realization (sowing dates, plant density, pest control). But fertility itself is not created in the field—it is delivered to the field by the soil's inherent property. An outstanding breeder can create a variety that better utilizes phosphorus from inaccessible compounds, but he will not create phosphorus in the soil. He will only "teach" the plant to better use what is there.
Why is This Important for Understanding Sustainability?
Recognizing that fertility is a property of the soil has profound implications for land resource management.
1. Fertility can be destroyed. If it is a property of the soil, then it can be lost—through erosion, dehumification, salinization, and compaction. The loss of fertility is a change in the soil itself, its internal organization.
2. Fertility can be restored, but slowly. Restoring fertility means restoring the properties of the soil, not just applying fertilizers. This takes time, organic matter, and structure formation.
3. Fertility is a common foundation for all crops. That is why the basis of agriculture is care for the soil, not just for the plants. Sustainable agriculture begins with the preservation and enhancement of soil fertility as a property of the soil itself.
To summarize: fertility is not the ability of a plant to absorb elements, nor the result of agronomic practices. It is a fundamental property of the soil, its internal capacity to meet the needs of plants. Plants, agrochemistry, and crop science only determine how fully this potential will be realized in a particular yield. Understanding this distinction is the basis for correctly diagnosing soil problems and developing strategies for their sustainable management.
Key takeaways from Chapter 2:
1. Fertility is an attribute of the soil as an independent natural body, existing independently of the presence of plants.
2. The distinction between potential (natural, inherent in the soil) and effective (realized in the yield) fertility clearly separates the soil property from the result of its use.
3. Fertility is ecologically specific: the same soil is fertile for some plants and infertile for others, determined by the properties of the soil itself (pH, texture, humus).
4. Agrochemistry and crop science are management tools for fertility, not its creators. They affect effective fertility without changing the potential (or changing it only in the long term).
5. Recognizing fertility as a property of the soil obliges us to responsible management of soil resources, since the loss of this property is the loss of the very basis of agricultural production.
3. What Constitutes Fertility?
Integration of Knowledge: Fertility as a Systemic Property
Now that we have established that fertility is a fundamental property of the soil itself, a natural question arises: what specific components does it consist of? Can fertility be measured by a single indicator, such as humus content or nitrogen reserves?
The answer is no. Fertility is a systemic, integrative property that arises from the interaction of many factors. It is similar to human health: it cannot be reduced to a single indicator like temperature or blood pressure. Health is the result of the coordinated work of all body systems in their interrelation.
Similarly, fertility is the result of the balanced work of all soil components. In this chapter, we need to show how the knowledge you gained in previous modules (soil physics, chemistry, biology) integrates into a unified understanding of fertility.
The level of potential soil fertility is determined by: humus content and its quality... nutrient content... particle size distribution... composition of exchangeable cations... microbiological and enzymatic activity
(Mukha et al., 2003, p. 186).
Let's examine these components sequentially.
1. Physical Factors of Fertility
The physical properties of the soil create the environment in which all chemical and biological processes take place. They determine whether roots have space to grow, whether there is enough air for respiration, and whether water can infiltrate and be retained in the soil.
Particle Size Distribution
The ratio of sand, silt, and clay particles is like the "skeleton" of fertility. It determines many key characteristics:
- Water-holding capacity: clayey soils retain more water than sandy ones (Weil & Brady, 2017).
- Drainage: sandy soils quickly transmit water, clayey ones slowly.
- Absorption capacity: clay particles and organic matter (humus) have a negative charge and hold cations (Ca²⁺, Mg²⁺, K⁺, NH₄⁺) in forms available to plants (Foth & Ellis, 1997). This is a manifestation of the cation exchange capacity (CEC).
The highest sorption is possessed by soils with high humus content, heavy particle size distribution, rich in montmorillonite...
(Valkov et al., 2004, p. 486).
Soil Structure
Structure is the ability of the soil to form aggregates—clods into which individual particles combine. This is a key element of fertility, as it is structure that creates:
- The optimal ratio of solid, liquid, and gaseous phases. In a well-structured soil, about 50% of the volume is pores, about half of which are filled with water and half with air (Weil & Brady, 2017).
- Water permeability and aeration. Aggregates create a system of macro- and micropores: large pores ensure rapid drainage of excess water and gas exchange, while small pores retain moisture for plants.
- Resistance to erosion and compaction. Aggregates, bound by humus and root exudates, resist the destructive action of raindrops and machine loads.
Good humus content... granular-cloddy structure and favorable agrophysical properties, large reserves of nutrients—all this is the result of the chernozem soil-forming process
(Mukha et al., 2003, p. 195).
Bulk Density and Porosity
Soil density (bulk density) directly affects root penetrability. Soil compaction is one of the most serious problems in modern agriculture. At densities above 1.5 g/cm³ for many soils, root growth is severely hindered (Troeh & Thompson, 1993). This is not just "hard" soil—it is soil that has lost part of its fertility due to the destruction of structure and reduction of pore space.
2. Water and Air Regimes
Water and air are the environment in which roots and microorganisms live. Their ratio and availability determine whether the fertility potential will be realized.
Water as the Basis of Soil Life
Water, air, heat are the most important components of soil fertility
(Valkov et al., 2004, p. 438).
Water performs several critical functions in the soil:
1. Solvent for nutrients. Most elements (except gaseous ones) are absorbed by plants from the soil solution in ionic form (Foth & Ellis, 1997; Eash et al., 2016).
2. Medium for microbiological processes. Microorganisms that decompose organic matter and release nutrients are active only when sufficient moisture is present.
3. Transport medium. The mass flow of water moves toward the roots (transpiration), delivering dissolved nutrients—primarily N, Ca, Mg, S (Foth & Ellis, 1997; Weil & Brady, 2017).
But water should not be excessive. With waterlogging, pores fill with water, displacing air—and oxygen starvation occurs.
Air—The Breath of the Soil
Plant roots, like human lungs, breathe. In the process of aerobic respiration, they absorb oxygen and release carbon dioxide. If there is not enough oxygen in the soil, roots cannot function normally—even with all nutrients present.
"Fertile soil should give high yields... but the yield can be low even on rich soil with a lack of air" (Troeh & Thompson, 1993, p. 11).
Soil air differs in composition from atmospheric air: it usually contains significantly more carbon dioxide and less oxygen due to the respiration of roots and microorganisms. Good aeration is achieved when the oxygen content in the soil air is at least 10-12%.
3. Chemical Factors of Fertility
The chemical properties of the soil are its "chemical kitchen," where some substances are transformed into others, and elements move from unavailable to available forms.
Organic Matter and Humus
Humus is perhaps the most important component of fertility. Its role is multifaceted:
1. Absorption capacity. Humus has a high cation exchange capacity—from 50 to 200 cmol(c)/kg (Baldock, 2012), which is several times higher than that of clay minerals. It retains cations (K⁺, Ca²⁺, Mg²⁺, NH₄⁺) and prevents their leaching.
2. Source of nutrients. During the mineralization of humus (decomposition by microbes), nitrogen, phosphorus, sulfur, and other elements are released in forms available to plants (Eash et al., 2016).
3. Improvement of structure. Humus binds particles into aggregates, improving the water-air regime.
4. Buffering capacity. Humus moderates sharp changes in pH (acidity), protecting plants from extreme values (Baldock, 2012).
"Humus reserves affect the reserves of nitrogen and other nutrients and growth-stimulating substances, the absorption capacity of the soil, structural state, and agrophysical characteristics" (Mukha et al., 2003, p. 186).
Reaction of the Environment (pH)
pH is one of the main regulators of nutrient availability. At different pH values:
- In acidic environments (pH < 5.5), the availability of phosphorus, calcium, magnesium, and molybdenum decreases; meanwhile, toxic forms of aluminum and manganese may accumulate (Weil & Brady, 2017; Eash et al., 2016).
- In alkaline environments (pH > 7.5), the availability of phosphorus, iron, zinc, copper, manganese, and boron decreases.
- In the pH range of 6.0–7.0, most elements are in forms most available to plants (Weil & Brady, 2017).
The pH optimum for most agricultural crops is in the slightly acidic and neutral range
(Scheffer et al., 2018).
Nutrients
Soil fertility is directly determined by the reserves of available macro- and micronutrients. However, it is important to understand the difference between total content (total amount of an element in the soil) and available content—what plants can actually absorb.
Elements exist in the soil in different forms (Eash et al., 2016):
- Minerals—slowly available, released only through weathering.
- Exchangeable cations and anions—held on the surface of colloids (clay, humus), available through ion exchange.
- Soil solution—the most available form, but its reserve is extremely small.
- Organic matter—released upon mineralization.
The highest effective fertility under optimal temperature and moisture conditions is possessed by chernozems
(Mukha et al., 2003, p. 194).
Absorption Capacity and Buffering Capacity
Absorption capacity (CEC) is the ability of the soil to retain cations on the surface of colloids. It depends on the humus content (high absorption capacity) and the type of clay minerals (Eash et al., 2016).
Buffering capacity—is the ability of the soil to resist changes in pH and the composition of the soil solution. A high buffering potential is the key to the stability of fertility under external influences (drought, acid rain, fertilizer application).
4. Biological Factors of Fertility
Soil is a living system. Billions of organisms in every gram of soil are not passive inhabitants but active participants in the processes that determine fertility.
Microorganisms
Microorganisms are the "invisible workers" of fertility. Their functions are critically important:
1. Mineralization of organic matter. Converting unavailable forms (humus, fresh organic matter) into available ions (NO₃⁻, NH₄⁺, H₂PO₄⁻, SO₄²⁻).
2. Nitrogen fixation. Nitrogen-fixing bacteria (nodule and free-living) convert atmospheric molecular nitrogen (N₂) into compounds available to plants (Eash et al., 2016).
3. Decomposition of toxins. Many microorganisms participate in the detoxification of pollutants (Valkov et al., 2004, p. 482).
4. Agronomically useful processes. Nitrification (conversion of NH₄⁺ to NO₃⁻), denitrification, sulfate reduction, etc.
Microorganisms are the main "processors" of organic matter. They mineralize humus, converting elements into forms available to plants
(Mukha et al., 2003, p. 186).
Soil Fauna
Worms, insects, nematodes—are the "engineers" of soil structure. Their activities include:
- Creation of macropores. Worm and root burrows are channels for water and air.
- Mixing of organic residues. Moving organic matter deeper into the profile, shredding it, and mixing it with the mineral part (Baldock, 2012).
- Activation of microbiological processes. Processing organic residues through the digestive system.
Soil Solution—The "Node" of Interaction of All Factors
All these factors—physical, chemical, biological—converge in the soil solution. This is the environment from which plants directly receive nutrition. The soil solution is not just water; it is a complex solution of ions, organic acids, gases, and other substances.
- It is here that ions emerge from the surface of colloids into an available form.
- It is here that microorganisms secrete enzymes and organic acids.
- It is here that "buffering" occurs—regulating the concentration of ions when they are consumed by plants.
Plants absorb elements from the soil in ionic forms, and these ions are in the soil solution—the most available form
(Eash et al., 2016, p. 8).
Unity and Interconnection of Factors
All the factors described—physical, water-air, chemical, and biological—do not exist in isolation. They form a unified system where a change in one component entails changes in all the others.
This can be represented as a diagram:
Structure → Water-air regime → Microbiological activity → Mineralization of organic matter → Supply of available elements to the soil solution → Plant nutrition → Supply of organic matter to the soil → Influence on structure (closing the cycle).
Or, as Valkov et al. (2004, p. 436) wrote: Soils have a special organomineral composition... they acquire a specific property—fertility—the ability to ensure plant growth and productivity
. This property is born at the intersection of the mineral and organic, the living and non-living, in the endless cycle of substances.
Therefore, when assessing fertility and planning measures to increase (or restore) it, we must take into account all these factors in their interrelationship. It is impossible, for example, to improve the chemical composition of the soil while maintaining poor structure. It is impossible to add organic matter and ignore biological activity. Fertility is a holistic property of the soil system.
Link with Humus Content: A Key Integral Indicator
Of all soil properties, humus content (or organic carbon) is the most integral indicator of fertility. Why?
1. Humus is closely linked to soil physics. Its content determines the ability to aggregate, structure, and water-holding capacity.
2. Humus is the basis of chemical fertility. It determines CEC, buffering capacity, and reserves of nitrogen and other elements.
3. Humus is an indicator of biological activity. Its formation and transformation are the result of the work of soil biota.
Good humus content... near-neutral or neutral reaction of the soil solution, calcium saturation, high buffering capacity, granular-cloddy structure and favorable agrophysical properties, large reserves of nutrients—all this is the result of the chernozem (sod) soil-forming process
(Mukha et al., 2003, p. 195).
Humus content is like an "integral portrait" of fertility. Therefore, any fertility management ultimately comes down to managing the content and quality of soil organic matter—through crop rotations, organic and mineral fertilizers, and tillage.
Summary: Fertility as a Result of Balanced Interaction
Let's summarize.
Fertility is not reducible to any one component. It is the result of a complex and balanced interaction of:
- Physical properties (structure, particle size distribution, density), ensuring the root environment.
- Water and air regimes, determining root respiration and water availability.
- Chemical properties, primarily humus content and cation exchange capacity, which create the nutrient potential.
- Biological activity, which carries out the conversion of unavailable substances into available ones and maintains the cycle of elements.
All these components converge in the soil solution—that very "life-giving moisture" directly consumed by plants.
This is precisely why fertility management is not about "feeding" plants (that is the task of agrochemistry) nor just "tilling" the soil (that is the task of agronomy). It is integrated management of the entire soil system aimed at preserving and enhancing its ability to provide plants with everything they need in the long term.
Key takeaways from Chapter 3:
1. Fertility is composed of physical, water-air, chemical, and biological factors that are closely interrelated.
2. Soil structure and humus are the two central elements around which all fertility is organized.
3. The soil solution is the "node" of interaction of all factors and the environment from which plants receive nutrition.
4. All components of fertility form a unified system, where a change in one factor entails changes in all others.
5. Humus content is an integral indicator reflecting the state of all components of fertility and is therefore key for monitoring and management.
4. Soil as a Renewable but Limited Resource
Two Views of Soil: Capital or Consumable Material?
In previous chapters, we came to understand that fertility is a complex, integrative property of the soil, formed at the intersection of physical, chemical, and biological processes. A natural question arises: if fertility can be restored (by applying fertilizers, organic matter, improving structure), does that mean soil is an inexhaustible resource?
The answer is both "yes" and "no." Soil is capable of self-recovery; it is renewable—but only under certain conditions and within certain time scales. However, this renewability has strict limits, and ignoring them leads to irreversible degradation.
Due to its ability to self-repair, soil can, to some extent, resist degradation. But these limits are very narrow, and the rate of natural recovery is extremely slow compared to the rate of anthropogenic destruction
(Troeh & Thompson, 1993, p. 8).
Therefore, we must view soil simultaneously as both a renewable and a limited resource. This apparent contradiction is the key to understanding the modern problem of sustainable land use.
Why is Soil a Renewable Resource?
The renewability of soil is ensured by two main processes.
1. Natural Soil Formation
Soil is continuously formed from parent material under the influence of climate, topography, organisms, and time (Jenny, 1941, cited in Weil & Brady, 2017). This process is ongoing, replenishing fertility reserves within the natural cycle.
- Chemical weathering. Minerals gradually decompose, releasing nutrients (K, Ca, Mg, P, Fe, etc.) (Eash et al., 2016).
- Accumulation of organic matter. Dying plants and animals decompose, replenishing humus reserves (Baldock, 2012).
- Biological activity. Microorganisms and soil fauna transform organic residues into compounds available to plants, closing the cycle of elements.
Under natural conditions, soil fertility is inextricably linked with the biocenosis corresponding to these soils and is the result of the development of the natural soil-forming process
(Valkov et al., 2004, p. 445).
2. Anthropogenic Restoration
Humans can significantly accelerate the restoration of fertility:
- Application of organic and mineral fertilizers compensates for the removal of elements with the harvest (Eash et al., 2016; Mukha et al., 2003).
- Liming (adding lime) neutralizes acidity and improves the availability of phosphorus, calcium, and magnesium (Scheffer et al., 2018).
- Gypsum application (adding gypsum) improves the structure of saline soils (Eash et al., 2016).
- Application of organic substances (manure, compost, green manure) increases humus content and improves physical properties (White, 2006).
- Agronomic practices (crop rotations, minimum tillage) support structure and biological activity (Troeh & Thompson, 1993).
By influencing the soil, humans not only increasingly use natural soil resources, increasing effective fertility, but also significantly change the potential capabilities of the soil—its potential fertility
(Mukha et al., 2003, p. 185).
Thus, thanks to both natural and artificial processes, fertility can be maintained and even increased—within certain limits.
Why is Soil a Limited Resource?
The limitation of soil as a resource manifests in several aspects: temporal, spatial, and functional.
1. Soil Formation Time
Soil formation is an extremely slow geological process. The natural restoration of one centimeter of topsoil takes from 100 to 400 years (Troeh & Thompson, 1993; Weil & Brady, 2017).
Soil losses due to erosion, however, can occur in a single season—during a rainstorm or dust storm.
The formation of one centimeter of topsoil can take from 100 to 400 years. The loss of this layer due to erosion, however, can occur in a single season
(Troeh & Thompson, 1993, p. 8).
This means that the rates of soil destruction are several orders of magnitude higher than the rates of its recovery. On the scale of a human lifetime, soil is practically a non-renewable resource.
2. Limited Area
The area of the Earth's surface suitable for agriculture is finite and has already been almost completely utilized.
- Total land area is about 13.4 billion hectares.
- Of this, about 1.5 billion hectares are used as arable land (approximately 11%) (Troeh & Thompson, 1993; Weil & Brady, 2017).
- Expansion of arable land is possible only through deforestation, drainage of wetlands, or development of marginal lands—which is often associated with environmental risks.
- Every year, significant areas of fertile land are irretrievably lost to construction, roads, and industrial facilities.
The best agricultural lands are often found under cities and industrial facilities
(Troeh & Thompson, 1993, p. 348).
The area of agricultural land per capita is continuously shrinking, while the demand for food is growing. This creates enormous pressure on the remaining soils, demanding increasingly intensive yields.
3. Irreversibility of Many Degradation Processes
Some types of soil degradation are practically irreversible in the foreseeable future:
- Erosion. Loss of the top, most fertile layer (Valkov et al., 2004, pp. 465–466).
- Dehumification. A sustained decline in humus content, which entails deterioration of structure, absorption capacity, and nitrogen reserves (Mukha et al., 2003, p. 477).
- Salinization and alkalinization. Accumulation of salts in the root zone, especially under improper irrigation (Eash et al., 2016; Valkov et al., 2004, pp. 472–474).
- Chemical contamination. Heavy metals, pesticides, petroleum products can persist in the soil for decades and centuries (Valkov et al., 2004, pp. 476–483).
- Physical degradation. Compaction, destruction of structure, crust formation (White, 2006).
Degradation and complete destruction of soil can occur both as a result of natural phenomena... and as a result of human economic activity
(Valkov et al., 2004, p. 461).
Many of these processes have no reverse course or require centuries and enormous capital expenditures for their restoration.
4. Exhaustibility of Individual Fertility Components
Some components of fertility are also limited:
- Phosphorus—a non-renewable resource, the planet's reserves of which are limited and could be exhausted within a few decades or centuries at current consumption rates (Weil & Brady, 2017, Chapter 14).
- Humus—can be restored, but only with the input of organic matter; under intensive agriculture, its content often steadily declines.
- Biological diversity—recovery of soil biota after degradation can take many years.
Soil in the Context of Sustainable Development
The modern understanding of soil as a limited resource has led to the formation of the concept of sustainable soil management. This concept underlies many international documents, including:
- FAO World Soil Charter (1982, revised in 2015).
- European Soil Protection Strategy (2006).
- National legislation.
The main principles of sustainable soil management are:
1. Irreplaceability. Soil fertility cannot be replaced by any technology (hydroponics—only for limited crops).
2. Resource limitation. Soil is a finite resource, and its use must be rational.
3. Necessity of reproduction. To preserve fertility, it is necessary to return to the soil what is taken from it (the law of return).
4. Prevention of degradation. It is easier to prevent the loss of fertility than to restore it.
5. Accounting for time. The rate of soil recovery is incomparably slower than the rate of its destruction, so the rate of degradation must be minimized.
The Paradox of Soil Fertility in the Anthropocene
The modern geological epoch, called the Anthropocene, is characterized by the dominant influence of humans on all natural processes, including soil formation (Richter & Tugel, 2012).
Humanity has become the main factor in soil formation and can cause changes in soils through individual events or long-lasting phenomena
(Richter & Tugel, 2012, p. 38-2).
Today we face a paradox:
- On the one hand, our knowledge and technology allow us to sharply increase soil fertility (breeding, fertilizers, reclamation, irrigation, precision farming).
- On the other hand, anthropogenic pressure on soils (intensification, urbanization, pollution) leads to their accelerated degradation, reduced fertility, and even complete loss.
The result of human economic activity can be both improvement of the original virgin soils and their deterioration, a decrease in potential and effective fertility
(Mukha et al., 2003, p. 185).
We can, using modern technology, obtain high yields on soils with low natural fertility. But the price of this is often an additional burden on the soil, which leads to its degradation. Conversely, the irrational use of even the most fertile chernozems leads to their depletion.
This is the central contradiction of modern agriculture: we can temporarily increase yields, but in the long term, we risk losing the very basis of fertility.
This is precisely why the transition to sustainable soil management is not just a "good idea" but an urgent necessity for the survival of human civilization.
Summary: Soil—Capital We Must Not Consume but Multiply
Let's summarize.
Soil is simultaneously a renewable and a limited resource:
- Renewability is ensured by natural soil formation and the possibility of anthropogenic restoration (fertilizers, organic matter, reclamation).
- Limitation is determined by:
- the extremely slow rate of natural formation (100–400 years per 1 cm of topsoil);
- the finite area of suitable land;
- the irreversibility of many degradation processes (erosion, dehumification, salinization, contamination, compaction);
- the exhaustibility of individual components (e.g., phosphorus).
On the scale of a human lifetime, soil is a practically non-renewable resource. Therefore, the main task of modern agriculture is not just to obtain a harvest but to preserve and enhance soil fertility for future generations.
This is the essence of sustainable soil management—the topic of the next chapter.
Key takeaways from Chapter 4:
1. Soil is renewable thanks to natural soil formation and anthropogenic restoration.
2. However, this renewability is extremely limited in time (hundreds of years for recovery) and in area (suitable land is finite).
3. Many types of degradation (erosion, dehumification, salinization, contamination, compaction) are practically irreversible in the foreseeable future.
4. In the Anthropocene era, humans have become the main factor in soil formation but often accelerate degradation rather than restoration.
5. Therefore, soil should be considered a non-renewable resource on the scale of a human lifetime, requiring especially careful treatment.
6. Sustainable soil management is not a choice but a necessity, driven by the finiteness and vulnerability of the soil resource.
5. What is Sustainable Soil Management?
From Exploitation to Sustainability: Why a Paradigm Shift is Necessary
Throughout most of the history of agriculture, humans treated soil as an inexhaustible resource. The farmer took as much from the land as he could, and when yields fell, he simply moved to a new plot, leaving the depleted lands for "self-recovery" (Troeh & Thompson, 1993; White, 2006). Such a strategy was possible while population density was low and free land was available. Today, the situation has changed radically.
In the 20th century, the intensification of agriculture, the "Green Revolution," and the widespread use of fertilizers and pesticides made it possible to dramatically increase food production. However, the price of this success was high:
- Accelerated soil erosion (Weil & Brady, 2017, Ch. 17; Valkov et al., 2004, pp. 465–466).
- Decrease in organic matter content (dehumification) (Mukha et al., 2003, p. 477).
- Salinization and alkalinization of irrigated lands (Eash et al., 2016, Ch. 9; Valkov et al., 2004, pp. 472–474).
- Contamination with heavy metals and pesticides (Valkov et al., 2004, pp. 476–483).
- Compaction and destruction of structure (White, 2006, pp. 245–246).
- Loss of soil biological diversity (Weil & Brady, 2017, Ch. 20).
As a result of economic activity, soil often loses its fertility, degrades, or is even completely destroyed. This happens when human activity is irrational and environmentally unsound
(Valkov et al., 2004, p. 461).
It became clear that the traditional strategy of "maximizing yields at any cost" leads to depletion and degradation of the soil resource. A new paradigm emerged—sustainable soil management.
Definition of Sustainable Soil Management
In its most general form, sustainable soil management (SSM) is a system of measures aimed at preserving and enhancing soil fertility, preventing its degradation, and ensuring long-term productivity with minimal negative impact on the environment.
A more formal definition is given in FAO documents (FAO, 2015): sustainable soil management is the use of soil resources in such a way as to maintain or increase their productivity, preserve or improve environmental quality, and contribute to human well-being, without undermining the soil's ability to perform its ecosystem functions for future generations.
In the Russian tradition, this concept is closely linked to soil protection and rational land use.
Soil protection and rational use is a system of measures aimed at protecting, improving, and rationally using lands, increasing soil fertility, and maintaining the sustainability of the biosphere as a whole
(Valkov et al., 2004, p. 461).
Thus, sustainable soil management is not just a set of agronomic practices but a systemic strategy based on a deep understanding of soil processes and ecological laws.
Principles of Sustainable Soil Management
Unlike specific agrotechnologies (tillage, crop rotations, fertilizers), which are studied in other courses, sustainable management is based on fundamental principles. Let's examine them in more detail.
1. Conservation and Improvement of Soil Functions
Soil performs many ecosystem functions that go far beyond a simple "substrate for plants" (Weil & Brady, 2017, Ch. 1; Scheffer et al., 2018, Ch. 1). Among them:
- Productive function—providing plants with water, nutrients, and physical support.
- Regulatory function—filtration, buffering, transformation of pollutants, regulation of water and gas regimes.
- Biotopic function—habitat for a huge diversity of organisms.
- Informational function—archive of natural and cultural history (archaeological and paleontological evidence).
Sustainable management requires that all these functions be preserved, not just the productive one. For example, one cannot allow soil that provides high yields to lose its ability to purify water or support biodiversity.
2. Prevention of Degradation
It is much easier to prevent degradation than to later restore the soil. This is a key principle repeatedly emphasized in the literature (Valkov et al., 2004; Mukha et al., 2003; Weil & Brady, 2017).
- Prevention of erosion. Maintaining plant cover, contour tillage, creating buffer strips, minimum tillage.
- Prevention of dehumification. Ensuring sufficient input of organic matter (crop residues, manure, green manure).
- Prevention of salinization. Proper irrigation, drainage, quality control of irrigation water.
- Prevention of compaction. Limiting soil loads, using technologies with controlled traffic.
- Prevention of chemical contamination. Control of pesticide and fertilizer application, monitoring of heavy metal content.
Soil protection from pollution... consists of the following. It is most advisable not to allow soil pollution... since their removal from the soil is a very difficult task
(Valkov et al., 2004, p. 478).
3. Maintenance and Increase of Organic Carbon Content
Soil organic matter is not only a source of nutrients but also the basis of physical, chemical, and biological fertility. Sustainable management requires:
- Preserving and, where possible, increasing soil organic carbon stocks.
- Using crop rotations that include perennial grasses and green manures.
- Applying organic fertilizers (manure, compost) and, where possible, biochar (Weil & Brady, 2017, Ch. 20).
- Reducing the intensity of tillage to minimize humus mineralization.
The decrease in soil organic carbon content is one of the main causes of degradation. Restoring the carbon pool is a key task of sustainable management
(Baldock, 2012, p. 11-36).
Moreover, carbon accumulation in soils is one way to mitigate climate change (carbon sequestration). This aspect is gaining increasing importance in the global environmental agenda.
4. Preservation of Structure and Prevention of Compaction
Good structure is the basis of the water-air regime. Sustainable management requires:
- Minimizing mechanical loads on the soil, especially when wet.
- Using technologies that reduce compaction (low-pressure tires, controlled traffic).
- Maintaining high organic matter content, which binds aggregates.
- Encouraging the activity of soil fauna (worms, insects), which create macropores.
Good soil structure is crucial for water infiltration, aeration, and root penetrability. Its destruction is one of the serious problems of modern agriculture
(White, 2006, pp. 245–246).
5. Maintenance of Biological Activity and Diversity
Soil biota is the "engine" of substance transformation processes. Sustainable management promotes:
- Preserving the diversity of microorganisms and soil fauna.
- Creating favorable conditions for their vital activity (sufficient moisture, aeration, input of organic matter).
- Minimizing the use of toxic pesticides that suppress beneficial microflora.
Microorganisms are the main "processors" of organic matter. Without them, the cycle of substances in the soil would be impossible
(Mukha et al., 2003, p. 186).
6. Adaptation to Local Conditions
There are no universal solutions in soil management. Different soils, climates, topography, and cultural traditions require different approaches. Sustainable management is always adaptive management, taking into account specific conditions:
- Soil type (chernozem, podzol, chestnut, solonetz, etc.)—each has its own fertility characteristics and vulnerabilities (Mukha et al., 2003, Ch. 16).
- Climatic conditions (humidity, temperature, length of growing season).
- Topography (slopes, plains, floodplains).
- Economic and social conditions (resource availability, technology level, markets).
Agro-production groupings of soils... have a specific territorial confinement and their own regional level
(Valkov et al., 2004, p. 454).
The Concepts of "Soil Health" and "Soil Quality"
In modern science and practice, the terms "soil health" and "soil quality" are increasingly used. These concepts are closely related to sustainable management but have different emphases.
Soil Quality
Soil quality is the ability of the soil to perform specific functions within an ecosystem, support plant productivity, regulate water flows, and protect the environment (Weil & Brady, 2017, Ch. 20). This concept is more functional and measurable.
Soil quality is assessed by a set of indicators:
- Physical: structure, density, water permeability, aggregate stability.
- Chemical: pH, humus content, available forms of elements, cation exchange capacity.
- Biological: microbial biomass, enzymatic activity, soil respiration, abundance and diversity of organisms.
Soil quality describes the properties that make the soil suitable for performing certain functions within the framework of the six main ecological roles of soils.
(Weil & Brady, 2017, p. 1002).
Soil Health
Soil health is a broader concept that emphasizes the self-regulation, resilience, and viability of the soil as a living system (Weil & Brady, 2017, pp. 1001–1002).
A healthy soil is one that:
- Has high biological activity and diversity.
- Is capable of resisting stresses (drought, diseases, pollution) and recovering from them (resilience).
- Is in a state of dynamic equilibrium, where the cycles of substances are balanced.
- Does not show symptoms of "disease": erosion, compaction, accumulation of toxins, reduced productivity.
Soil health implies self-regulation, stability, resilience, and the absence of signs of stress in the soil as an ecosystem.
(Weil & Brady, 2017, p. 1001).
Interestingly, the concept of "soil health" is often associated with a holistic, ecosystem approach, while "soil quality" is associated with a more utilitarian, functional assessment. However, in practice, these terms are often used interchangeably.
Although these terms are often used as synonyms, they actually denote two different concepts.
(Weil & Brady, 2017, p. 1001).
Practical Significance for Management
Both concepts are important for sustainable management:
- Assessment of soil quality allows diagnosis of the current state and tracking of changes (monitoring).
- The soil health concept sets the strategic goal of management: not just to maintain productivity but to ensure the long-term viability of the soil ecosystem.
In Russia, this idea is reflected in the concept of "ecological state of lands" and in the system of criteria for ecological disaster zones (Mukha et al., 2003, pp. 480–484).
Sustainable Management as a Systems Approach
In summary, sustainable soil management is not a set of recipes but a systems approach that:
1. Recognizes soil as a living system, not just a substrate.
2. Considers all soil functions (productive, regulatory, biotopic, informational), not just yield.
3. Strives for balance between the use and reproduction of fertility.
4. Focuses on the long-term perspective, not on short-term gain.
5. Adapts to local conditions and continuously learns based on monitoring.
Mitigating the contradictions between natural and anthropogenic systems is possible only within the framework of stable socio-economic development that does not destroy its natural basis
(Mukha et al., 2003, p. 475).
Sustainable soil management is not "another agronomic practice" but a philosophy of land use that should permeate all agronomist's decisions: from crop selection and tillage to fertilization and plant protection systems.
Summary
Sustainable soil management is a system of measures aimed at preserving and improving all soil functions while minimizing negative environmental impact, ensuring long-term productivity and environmental sustainability.
Key principles:
1. Conservation of all soil functions.
2. Prevention of degradation.
3. Maintaining and increasing organic carbon stocks.
4. Preserving structure and preventing compaction.
5. Maintaining biological activity and diversity.
6. Adaptation to local conditions.
The concepts of "soil quality" and "soil health" serve as the basis for assessment and monitoring, with the former being more functional and the latter more integrative and ecosystem-oriented.
Ultimately, sustainable management is not just an agronomic task but a global strategy for human survival under conditions of limited soil resources and growing needs.
Key takeaways from Chapter 5:
1. The traditional exploitative model of agriculture is unsustainable in the long run.
2. Sustainable soil management is a systemic strategy, not a separate agronomic practice.
3. Its principles cover all functions of the soil, not just the productive one.
4. Prevention of degradation is the most important principle, as restoration takes centuries.
5. Organic matter and structure are central objects of management.
6. "Quality" and "health" of soil are interrelated but different concepts: quality is a functional assessment, health is integrative and ecosystem-oriented.
7. Sustainable management adapts to local conditions and requires constant monitoring.
6. Fertility and Soil Health
From Property to State: Evolution of the View on Soil
In classical soil science, fertility was traditionally viewed as the soil's ability to supply plants with nutrients, water, and physical support. This was a utilitarian, productive characteristic. However, as knowledge accumulated about the complexity of soil processes and the role of soil in global ecosystems, it became clear that fertility is just one facet of a much broader concept—soil health.
Soil health implies self-regulation, stability, resilience, and the absence of stress symptoms in the soil as an ecosystem. Soil health describes the biological integrity of the soil community—the balance among organisms in the soil, as well as between soil organisms and their physical and chemical environment.
(Weil & Brady, 2017, p. 1001).
Soil health is the integrative state of the entire soil system, which includes not only the ability to produce a yield (fertility) but also the ability to self-regulate, resist stresses, maintain biological diversity, and perform all ecosystem functions. Fertility, therefore, is a necessary but not sufficient condition of soil health.
This distinction has profound practical meaning. A soil can be fertile today—producing high yields thanks to intensive application of fertilizers and pesticides. But its health may be undermined: structure destroyed, biological activity suppressed, resistance to drought or diseases reduced. Such a soil is "sick," even if it is temporarily productive.
A fertile soil provides a steady supply of dissolved mineral nutrients... but a healthy soil is not just fertile: it is resilient, self-regulating, and capable of maintaining its functions in the long term.
(Weil & Brady, 2017, p. 22).
Thus, the task of the modern agronomist is not just to maintain fertility but to restore and maintain soil health, which will automatically ensure sustainable fertility.
What is Soil Health and What Does It Consist Of?
Soil health is a state in which the soil as a living system is capable of performing all its ecological functions in full and at the same time maintaining resilience to external influences. It consists of three interrelated components:
1. Physical Health
- Good structure—presence of aggregates resistant to destruction, providing an optimal ratio of pores of different sizes.
- Sufficient porosity—ensures aeration, water permeability, and root penetrability.
- Absence of compaction—bulk density does not exceed critical values for the given soil type.
Poor physical health manifests as crust formation, water stagnation, poor drainage, and restricted root growth.
2. Chemical Health
- Balanced pH—in the range of 6.0–7.0 for most crops.
- Sufficient organic matter content (humus) and its quality.
- Presence of all necessary macro- and micronutrients in available forms with the absence of toxic concentrations.
- High cation exchange capacity and buffering capacity.
Chemical health not only ensures plant nutrition but also provides protection against pollution, as a healthy soil is capable of neutralizing and binding many toxins.
3. Biological Health
- High diversity and abundance of microorganisms (bacteria, fungi, actinomycetes, protozoa).
- Active soil fauna (worms, insects, nematodes).
- Balanced microbial communities—the ratio of functional groups (mineralizers, nitrogen fixers, cellulolytic, pathogenic).
- High enzymatic activity and intensity of organic matter transformation processes.
Soil fertility depends on microbiological and enzymatic activity, influencing the processes of transformation of organic and mineral compounds, the nutrient regime
(Mukha et al., 2003, p. 186).
All three components are closely interrelated. For example, poor structure (physical health) limits aeration, which reduces biological activity (biological health), which, in turn, slows down the mineralization of organic matter and the release of nutrients (chemical health). It is this interrelationship that makes soil health a systemic property that cannot be reduced to individual indicators.
Indicators of Soil Health
To assess soil health, sets of indicators have been developed to diagnose the state and track changes (Weil & Brady, 2017, Ch. 20). These indicators are divided into three groups, corresponding to the three aspects of health.
Biological Indicators
Biological indicators are most sensitive to changes and provide early information about disturbances:
- Microbial biomass carbon (MBC)—the total mass of living microorganisms. A decrease in MBC indicates stress.
- Soil respiration (CO₂ evolution)—the intensity of microbial metabolism. A decrease in respiration may indicate biota suppression.
- Enzymatic activity (dehydrogenase, urease, phosphatase, etc.)—reflects the intensity of specific biochemical processes.
- Active carbon (labile, easily oxidizable)—the most readily available part of organic matter for microorganisms.
- Potentially mineralizable nitrogen (PMN)—the soil's ability to release nitrogen for plants.
- Abundance and diversity of soil fauna (worms, nematodes, mites)—indicators of food web integrity.
Microbial biomass carbon, active carbon, mineralizable nitrogen, and qCO₂ (specific respiration) are among the most sensitive indicators of soil health.
(Weil & Brady, 2017, pp. 1003–1004).
Physical Indicators
- Aggregate stability (stability of aggregates in water)—a key indicator of structure.
- Bulk density—an indicator of compaction.
- Water permeability and infiltration capacity.
- Number and distribution of pores by size.
- Depth of the root zone and presence of a plow pan.
Aggregate stability is a good indicator of the physical state of the soil, as it accounts for the influence of organic matter, biological activity, and tillage methods.
(Weil & Brady, 2017, p. 1009).
Chemical Indicators
- pH—regulator of the availability of many elements.
- Total organic carbon (TOC) content—an integral indicator.
- CEC (cation exchange capacity) and base saturation percentage.
- Content of available forms of N, P, K, Ca, Mg, S and micronutrients.
- Electrical conductivity (EC)—an indicator of salinization.
- Absence of toxic concentrations of heavy metals and organic pollutants.
It is important that no single indicator can provide a complete assessment. Integral indices are used, such as the Soil Quality Index (SQI) or the Soil Management Assessment Framework (SMAF), which combine several indicators into a single numerical assessment (Weil & Brady, 2017, pp. 1005–1006; Box 20.1).
Soil Health and Resilience
One of the key aspects of soil health is its resilience—the ability to recover after disturbances (drought, waterlogging, mechanical loads, pollution). Resilience is contrasted with resistance (the ability not to change under influence), but both characteristics are important for sustainable management.
Soil resistance is the ability to maintain functional integrity under the influence of external factors, and resilience is the ability to restore functional and structural integrity lost after the impact of external factors or prolonged stress.
(Richter & Tugel, 2012, p. 38-8).
A healthy soil possesses:
- High resistance—it does not lose its functions under normal agronomic loads.
- High resilience—it recovers quickly after stress events (e.g., after drought or the passage of heavy machinery).
Resilience is ensured by:
- Biological diversity—the presence of many species duplicating functions allows the system to "survive" the loss of one component.
- High organic matter content—it improves structure, increases buffering capacity, and water-holding capacity.
- Developed root system of plants—roots create macropores and support aggregation, and also serve as a source of organic matter.
- Balanced microbial communities—they quickly respond to changes and restore their functions.
Resilience is a crucial component of soil health. A soil with high resilience quickly recovers from disturbances, while a soil with low resilience may remain degraded for a long time.
(Weil & Brady, 2017, pp. 1010–1011).
Loss of resilience is one of the first signs of deteriorating soil health, which can remain unnoticed against the background of temporarily high yields.
Fertility as Part of Soil Health
What is the place of fertility in the concept of soil health? It can be said that fertility is an integral, but not the only, component of health. Soil health includes fertility but goes beyond it, encompassing:
- Ability for self-regulation—maintaining balance between processes of accumulation and mineralization of organic matter, between absorption and release of elements.
- Ability for purification—neutralization and decomposition of pollutants.
- Ability to support biodiversity—creating conditions for the existence of many species.
- Ability for long-term functioning—preserving all ecosystem functions over decades and centuries.
In other words, fertility is the "productive" component of health, but a healthy soil must also be "clean," "living," and "stable."
Interestingly, in scientific literature, the concepts of "soil quality" and "soil health" are often used interchangeably, but many authors emphasize the distinction:
The term "soil health" is best applied to soil as an ecosystem, emphasizing its biological integrity and self-regulation, while "soil quality" has a more utilitarian character, focusing on the suitability of the soil for performing specific functions.
(Weil & Brady, 2017, pp. 1001–1002).
In the Russian tradition, this distinction is also reflected: "fertility" is a narrower, agronomic concept, while "ecological state" or "health" is broader, including all ecosystem functions (Valkov et al., 2004; Mukha et al., 2003).
Practical Significance: Managing Soil Health
The transition from managing fertility to managing soil health has important practical implications:
1. Shifting the Focus from "Treatment" to "Prevention"
Instead of reacting to symptoms (nutrient deficiency, diseases, compaction), sustainable management is aimed at creating conditions where such symptoms do not arise. This means:
- Regular monitoring of health indicators.
- Preventive measures (crop rotations, cover crops, organic fertilizers).
- Minimization of disturbing influences (tillage, heavy machinery).
2. Integration of Agronomic Practices
Managing soil health requires an integrated approach, where all practices (tillage, crop rotation, fertilization, plant protection) are considered in their interrelation. For example, a proper crop rotation not only restores structure and increases humus but also reduces the number of pathogens and pests and improves biological activity.
3. Use of Biological Indicators
Biological indicators (microbial biomass, respiration, enzymatic activity) are early signals of soil health disturbance, which can manifest long before a decline in yield. Regular monitoring of these indicators allows timely adjustment of management.
Biological indicators are often the first to show changes in soil condition, long before it affects its chemical or physical properties.
(Weil & Brady, 2017, p. 1004).
4. Restoration of Degraded Soils
If soil health is already impaired, management should be aimed at its restoration. This may include:
- Application of organic substances (compost, manure, green manure) to restore humus and biological activity.
- Use of cover crops to improve structure and prevent erosion.
- Application of biological products (microorganisms, mycorrhizal fungi) to accelerate biota recovery.
- Reclamation measures (liming, gypsum application, drainage) to eliminate chemical and physical limitations.
An example of successful soil health restoration is Terra Preta (anthropogenic chernozems of the Amazon), where ancient farmers maintained high fertility for millennia by adding charcoal, organic waste, and ash, creating sustainable soil health that persists to this day (Weil & Brady, 2017, Box 20.4).
Conclusion: Soil Health as the Foundation of Sustainable Agriculture
In this chapter, we have shown that fertility is an important but only one component of the broader concept of soil health. Healthy soil is not only fertile but also biologically active, structurally stable, self-regulating, capable of resisting stresses, and recovering from disturbances.
The transition from managing fertility to managing soil health requires:
- Understanding soil as a living ecosystem, not just a substrate.
- Using comprehensive indicators (physical, chemical, biological).
- Applying preventive, adaptive management strategies.
- Integrating all agronomic practices into a unified system.
- Continuous monitoring and adjustment.
Ultimately, it is soil health that ensures long-term and sustainable fertility—what is necessary for food security and environmental preservation in the Anthropocene.
Key takeaways from Chapter 6:
1. Fertility is the soil's ability to provide plants with life factors, while soil health is the integrative state of the entire soil ecosystem, including self-regulation, resilience, and the performance of all ecological functions.
2. Soil health consists of physical, chemical, and biological health, closely interrelated.
3. Soil health indicators include biological (microbial biomass, respiration, enzymes), physical (aggregate stability, density), and chemical (humus, pH, available elements) parameters.
4. Resilience—the ability to recover from stress—is a key characteristic of healthy soil.
5. Managing soil health is a preventive, integrative, and adaptive strategy that goes beyond traditional fertility management.
6. Ultimately, soil health is the foundation of sustainable fertility, capable of being maintained in the long term.
References
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