AP Environmental Science • Earth Systems and Resources

Soil Composition and Properties

Understanding the dynamic mixture of minerals, organic matter, water, and air that sustains terrestrial ecosystems.

A sprouting plant framed by Earth and recycling symbols.
Inside this lesson 9 sections 5 questions 6 figures

SECTION 1

Historical Context & Motivation

For millennia, civilizations have risen and fallen based on their relationship with soil—the thin veneer of weathered rock and organic material that blankets Earth's land surface. Ancient Mesopotamians irrigated fertile alluvial soils along the Tigris and Euphrates, yet salinization from poor drainage eventually rendered those soils barren, contributing to the decline of Sumerian agriculture. Despite this intimate dependence, the scientific study of soil as a distinct natural body did not emerge until the nineteenth century, when researchers began to view soil not merely as pulverized rock but as a living, layered system shaped by climate, organisms, topography, parent material, and time.

1840 • Liebig's Mineral Theory

Justus von Liebig published research demonstrating that plants derive mineral nutrients from soil, establishing the foundation of soil chemistry and the Law of the Minimum.

1883 • Dokuchaev's Soil Horizons

Russian geologist Vasily Dokuchaev published his study of Russian chernozem (black earth), proposing that soils form distinct horizontal layers—horizons—shaped by five soil-forming factors.

1930s • U.S. Dust Bowl

Massive wind erosion across the Great Plains exposed the catastrophic consequences of ignoring soil structure and organic matter, prompting creation of the Soil Conservation Service.

1975 • USDA Soil Taxonomy Published

The USDA's comprehensive classification system organized soils into 12 orders based on measurable properties, becoming the standard reference for soil science worldwide.

2015 • International Year of Soils

The United Nations declared 2015 the International Year of Soils, highlighting soil degradation as a global environmental crisis affecting food security and carbon cycling.

These milestones frame a central question for environmental science: What determines the composition, structure, and fertility of soil, and how do human activities alter these properties? Answering this question requires examining soil as a four-phase system of minerals, organic matter, water, and air—an approach that underpins every AP Environmental Science topic from agriculture to biogeochemical cycling.

SECTION 2

Core Principles & Definitions

Soil is fundamentally a mixture of four components whose proportions govern virtually every property relevant to plant growth, water filtration, and nutrient cycling. An idealized loam soil is approximately 45% mineral particles by volume, 5% organic matter (including humus and living organisms), 25% water, and 25% air. The solid fraction—minerals plus organic matter—creates a matrix of pore spaces that hold the water and air essential for root respiration and microbial activity.

1

Soil Texture

The relative proportions of sand (0.05–2.0 mm), silt (0.002–0.05 mm), and clay (<0.002 mm). Texture determines water-holding capacity, permeability, and nutrient retention.
2

Soil Structure

The arrangement of soil particles into aggregates (peds) bound by organic matter, clay, and microbial secretions. Good structure creates macropores for drainage and micropores for water retention.
3

Cation Exchange Capacity (CEC)

A measure of soil's ability to hold positively charged nutrient ions (Ca²⁺, K⁺, Mg²⁺) on negatively charged clay and humus surfaces. Higher CEC generally means greater fertility.
4

Soil pH

The concentration of H⁺ ions in soil solution, typically ranging from 4.0 to 8.5. pH influences nutrient solubility, microbial activity, and the availability of toxic metals like aluminum.
5

Porosity & Permeability

Porosity is the total volume of pore space; permeability is the rate at which water moves through interconnected pores. Clay soils have high porosity but low permeability; sandy soils exhibit the reverse.

A pale root hair remains continuous with the root epidermis as it extends into cyan water films between layered mineral particles and dark soil organic material; separate air voids are visible.Soil surfaces can reversibly exchange counterions. One adsorbed Ca²⁺ exchanges with two H⁺ while conserving two negative surface sites, one calcium ion and two protons. The dashed surface associations represent electrostatic association.

Reversible cation exchange at a soil surface. Soil surfaces can reversibly exchange counterions. One adsorbed Ca²⁺ exchanges with two H⁺ while conserving two negative surface sites, one calcium ion and two protons. The dashed surface associations represent electrostatic association.Soil surfaces can reversibly exchange counterions. One adsorbed Ca²⁺ exchanges with two H⁺ while conserving two negative surface sites, one calcium ion and two protons. The dashed surface associations represent electrostatic association.

Illustrative sand-rich, clay-rich and loam soil columns accompany a separate equal-area model of wider and narrower pore throats. The exact comparison holds modeled void fraction fixed; it does not depict compaction.The same pore-area fraction can accompany different widths of connecting pore throats. Porosity and permeability therefore measure different properties, and some water held in very small pores is difficult for roots to extract.

Equal modeled void fraction does not imply equal pore-throat geometry.. The same pore-area fraction can accompany different widths of connecting pore throats. Porosity and permeability therefore measure different properties, and some water held in very small pores is difficult for roots to extract.The same pore-area fraction can accompany different widths of connecting pore throats. Porosity and permeability therefore measure different properties, and some water held in very small pores is difficult for roots to extract.

SECTION 3

Soil Composition & Horizon Diagram

Soil Horizon ProfileO Horizon – Organic LitterA Horizon – TopsoilE Horizon – Eluviation ZoneB Horizon – SubsoilC Horizon – Parent MaterialR Horizon – BedrockDecomposing leaves, rootsHumus-rich, high biological activityLeached of clays & mineralsAccumulation of clays, Fe, Al oxidesPartially weathered rock fragmentsUnweathered bedrockIdeal Loam by Volume45% Minerals5% Organic Matter25% Water25% Air
A typical soil profile shows six master horizons (O through R), each with distinct composition and function. The legend at the bottom shows the ideal volumetric composition of a loam soil: 45% minerals, 5% organic matter, 25% water, and 25% air.

The soil profile depicted above illustrates the concept of horizon differentiation—the vertical layering produced by weathering, leaching, and biological activity over time. The O horizon consists primarily of freshly fallen and partially decomposed organic debris. Beneath it, the A horizon (topsoil) is the zone of greatest biological activity where humus mixes with mineral grains. The E horizon experiences eluviation, the downward transport of dissolved or suspended material. These leached substances accumulate in the B horizon (subsoil) through illuviation. The C horizon is partially weathered parent material, and the R horizon is unaltered bedrock. On the AP exam, questions commonly ask students to identify which horizon would be most affected by erosion (A), which accumulates clay (B), or which represents the starting material from which the soil developed (C/R).

A forest soil cutaway with roots and litter accompanies authored O,A,E,B,C horizon bands and a downward translocation arrow.Soil horizons reflect litter inputs, mixing, upper-horizon export and deeper accumulation. Dissolved leaching differs from suspended-clay translocation; profile depth and fertility depend on more than age.

Soil profiles reflect additions,transfers and transformations.. Soil horizons reflect litter inputs, mixing, upper-horizon export and deeper accumulation. Dissolved leaching differs from suspended-clay translocation; profile depth and fertility depend on more than age.Soil horizons reflect litter inputs, mixing, upper-horizon export and deeper accumulation. Dissolved leaching differs from suspended-clay translocation; profile depth and fertility depend on more than age.

SECTION 4

Soil-Forming Factors & Processes

The Five Soil-Forming Factors (CLOrPT)

Soil scientist Hans Jenny formalized the relationship between soil properties and the factors that control their development using the state-factor equation: S = f(Cl, O, R, P, T), where S is any soil property, Cl is climate, O is organisms (biota), R is relief (topography), P is parent material, and T is time. The mnemonic CLOrPT captures these five factors. Climate—particularly precipitation and temperature—is generally the most influential factor because it drives both the rate of chemical weathering and the type of vegetation present.

JENNY'S STATE-FACTOR EQUATION

S=f(Cl,O,R,P,T)S = f(Cl, O, R, P, T)

S = any measurable soil property (e.g., pH, texture, CEC); Cl = climate (precipitation, temperature); O = organisms (vegetation, microbes, fauna); R = relief/topography; P = parent material; T = time since pedogenesis began.

Four Major Pedogenic Processes

1

Addition

Materials added to the soil from external sources: organic litter falling on the surface, atmospheric dust deposition, and dissolved ions arriving in precipitation.
2

Loss (Removal)

Materials removed by erosion, leaching of soluble ions to groundwater, or volatilization of gases (e.g., N₂O from denitrification).
3

Translocation

Movement of materials within the profile. Eluviation moves clay and dissolved substances downward; bioturbation by earthworms moves material upward.
4

Transformation

Chemical or physical alteration in place: weathering of primary minerals to secondary clay minerals, decomposition of organic matter into humus.

These four processes operate simultaneously and at different rates depending on the five state factors. In a tropical environment with heavy rainfall and warm temperatures, transformation (chemical weathering) and loss (leaching) dominate, producing deeply weathered, nutrient-poor oxisols. In grasslands of temperate regions, addition of organic matter from dense root systems and moderate leaching produce the rich, dark mollisols that form the world's most productive agricultural soils.

SECTION 5

Soil Texture Triangle & Classification

Soil texture is determined by performing a particle-size analysis and plotting the percentages of sand, silt, and clay on the USDA soil texture triangle. This ternary diagram divides all possible combinations into twelve textural classes, from pure sand to heavy clay. The textural class governs many soil behaviors: sandy soils drain rapidly and warm quickly in spring but hold few nutrients, while clay-rich soils retain moisture and cations but may become waterlogged and difficult to till.

USDA Soil Texture Triangle (Simplified)100% Clay100% Sand100% SiltClaySandy ClaySilty ClayClay LoamSandy Clay LoamSilty Clay LoamLOAMSandy LoamSilt LoamSiltSand40-20-40% Sand axis runs lower-left → upper-right | % Clay axis runs bottom → top | % Silt axis runs lower-right → upper-leftGreen dot = ideal loam (≈40% sand, 20% clay, 40% silt). All three axes must sum to 100%.
Simplified USDA soil texture triangle showing the twelve textural classes. The green dot marks an ideal loam at approximately 40% sand, 20% clay, and 40% silt. On the AP exam, you may be asked to identify a textural class given percentages of sand, silt, and clay.
Textural ClassParticle SizeWater-Holding CapacityPermeabilityCEC
Sand0.05–2.0 mmLowHighLow
Silt0.002–0.05 mmModerateModerateModerate
Clay< 0.002 mmHighLowHigh
LoamMixedModerate–HighModerateModerate–High

Comparison of major textural classes and their properties

SECTION 6

Worked Example: Soil Analysis

Worked example

  1. 1

    Step 1 — Identify Given Values

    A soil sample contains 30% sand, 50% silt, and 20% clay by mass. The field has an area of 2 hectares. After a rainfall event, a percolation test yields an infiltration rate of 1.5 cm/hr.
  2. 2

    Step 2 — Determine Textural Class

    Using the USDA texture triangle: 30% sand, 50% silt, 20% clay places this sample in the silt loam region. Silt loam soils have moderate water-holding capacity and moderate permeability.
    Textural class: Silt Loam
  3. 3

    Step 3 — Calculate Total Water Infiltrated

    If a storm delivers 3 cm of rainfall over 2 hours at an infiltration rate of 1.5 cm/hr, the total infiltration capacity over 2 hours is 1.5 cm/hr × 2 hr = 3.0 cm. Since total precipitation (3 cm) equals infiltration capacity (3 cm), all water infiltrates and there is no surface runoff under these idealized conditions.
    Runoff = 0 cm (all precipitation infiltrates)
  4. 4

    Step 4 — Estimate Volume Infiltrated

    Volume = depth × area = 0.03 m × 20,000 m² (2 ha) = 600 m³ of water infiltrated into the soil.
    600 m³ infiltrated
  5. 5

    Step 5 — Interpret Environmental Significance

    If this same rainfall fell on compacted clay soil with an infiltration rate of 0.5 cm/hr, only 1.0 cm would infiltrate over 2 hours, generating 2.0 cm of runoff (= 400 m³). This illustrates why soil texture and structure directly influence flood risk, erosion, and groundwater recharge.

A close-up of soil aggregates marks a clump and pore space. A separate mineral-fraction bar shows 40 percent sand, 40 percent silt and 20 percent clay.The illustrative mineral fraction contains 40% sand, 40% silt and 20% clay, a loam composition. The bar shows those proportions; the separate aggregate image illustrates clumps and pore spaces. Texture alone does not establish field arrangement or permeability. Separate illustrative sample: 40% sand, 40% silt, 20% clay (loam). The worked example uses 30% sand, 50% silt, 20% clay (silt loam).

SECTION 7

Soil Degradation vs. Conservation

Soil degradation—through erosion, compaction, salinization, nutrient depletion, and contamination—is one of the most pressing environmental challenges of the 21st century. The United Nations estimates that roughly one-third of global soils are moderately to highly degraded. Understanding how soil properties change under different management regimes is essential for the AP Environmental Science exam and for real-world land management.

Degradation ProcessCauseConservation Strategy
Erosion (wind/water)Removal of vegetation, overgrazing, tillage on slopesContour plowing, terracing, cover crops, riparian buffers, no-till farming
CompactionHeavy machinery, livestock tramplingControlled traffic farming, reduced tillage, organic matter amendments
SalinizationIrrigation in arid regions, poor drainageDrip irrigation, salt-tolerant crops, improved drainage infrastructure
Nutrient depletionMonoculture, excessive harvesting without replenishmentCrop rotation, legume cover crops (nitrogen fixation), composting
AcidificationAcid deposition, nitrogen fertilizer overuseLiming (CaCO₃ application), balanced fertilization

Common soil degradation processes and conservation strategies

SECTION 8

Connections to Biogeochemical Cycles

Soil is not merely a substrate for plant growth—it is a critical nexus in the global carbon, nitrogen, and phosphorus cycles. The top meter of Earth's soils stores roughly 1,500 gigatons of organic carbon, more than twice the amount present in the atmosphere and all terrestrial vegetation combined. When soil is disturbed through deforestation, tillage, or drainage of wetlands, microbial decomposition accelerates and CO₂ is released, making soil management a significant variable in climate change mitigation.

CycleRole of SoilKey Processes
CarbonMajor terrestrial carbon reservoir; stores organic C as humusDecomposition, humification, root respiration, carbon sequestration
NitrogenMedium for N transformations; hosts nitrifying and denitrifying bacteriaNitrogen fixation, ammonification, nitrification, denitrification, leaching
PhosphorusPhosphorus cycles almost entirely through soil-rock interactions (no significant gas phase)Weathering of apatite, adsorption onto clay/Fe oxides, mycorrhizal uptake

Soil's role in major biogeochemical cycles

For the AP exam, expect questions linking soil properties to broader environmental outcomes. For instance, a low-CEC sandy soil in a heavily fertilized agricultural setting would be prone to nitrate leaching into groundwater, whereas a high-CEC clay soil retains cations more effectively but may become waterlogged and generate anaerobic conditions that promote denitrification and N₂O emissions—a potent greenhouse gas. Understanding these trade-offs is the hallmark of systems-level thinking in environmental science.

SECTION 9

Practice Problems

Question 1: CONCEPTUAL

Which soil horizon is characterized by the accumulation of clay, iron oxides, and organic compounds translocated from overlying horizons?
  • A. O horizon
  • B. A horizon
  • C. B horizon
  • D. C horizon
Show answer (C)
The correct answer is C (B horizon). The B horizon is the zone of illuviation where materials leached from above accumulate—including clay minerals, iron (Fe) and aluminum (Al) oxides, and humus. The O horizon (A) consists only of organic litter on the surface. The A horizon (B) is the topsoil where organic matter mixes with minerals but is a zone of eluviation (loss), not accumulation. The C horizon (D) is partially weathered parent material that has not undergone significant pedogenic processes like illuviation.

Question 2: BASIC CALCULATION

A soil sample has the following composition by mass: 55% sand, 30% silt, and 15% clay. Using the USDA texture triangle, which textural class does this soil belong to?
  • A. Sandy loam
  • B. Silt loam
  • C. Clay loam
  • D. Loam
Show answer (A)
The correct answer is A (Sandy loam). With 55% sand, 30% silt, and 15% clay, the dominant particle fraction is sand, and the clay content is too low for the loam or clay loam classes. On the texture triangle, this combination falls squarely in the sandy loam region. Silt loam (B) would require >50% silt. Clay loam (C) requires 27–40% clay. Loam (D) requires a more balanced distribution with 7–27% clay, 28–50% silt, and less than 52% sand—this sample's sand content is too high.

Question 3: INTERMEDIATE

A farmer notices that after switching to continuous corn monoculture and conventional tillage, soil organic matter dropped from 5% to 2% over 15 years. Which of the following best explains the primary mechanism for this decline?
  • A. Increased infiltration rate reduced microbial habitat
  • B. Tillage disrupted soil aggregates, exposing organic matter to accelerated microbial decomposition and oxidation
  • C. Corn plants absorb organic matter directly through their roots
  • D. Wind erosion preferentially removed mineral particles, concentrating clay
Show answer (B)
The correct answer is B. Conventional tillage physically breaks apart soil aggregates that normally protect organic matter within their interiors. Once exposed, this organic matter becomes accessible to aerobic microorganisms, and decomposition accelerates. Additionally, monoculture provides less diverse residue inputs than a diverse rotation. Option A is incorrect because tillage typically decreases (not increases) infiltration. Option C is wrong because plants do not absorb organic matter; they absorb dissolved inorganic nutrients. Option D is incorrect because wind erosion preferentially removes lighter particles (fine silt, clay, and organic matter), not mineral particles specifically.

Question 4: APPLIED

Design an investigation to determine how soil texture affects water infiltration rate. Your response should include a testable hypothesis, identification of independent and dependent variables, a brief description of experimental procedure, and one control that must be held constant.
Show answer
Hypothesis (1 pt): If soil texture varies from sand to clay, then the infiltration rate will be highest in sandy soil and lowest in clay soil, because larger pore spaces in sand allow faster water movement. Independent variable (1 pt): Soil texture (e.g., pure sand, silt loam, clay). Dependent variable (1 pt): Infiltration rate measured as cm of water absorbed per hour (or time for a fixed volume to drain through the column). Procedure (1 pt): Pack three identical PVC cylinders (e.g., 10 cm diameter × 30 cm height, with mesh at the bottom) with sand, silt loam, and clay respectively at equal bulk density. Pour 500 mL of water onto each column simultaneously and measure the time for water to begin dripping from the bottom and the total volume collected in 30 minutes. Repeat with ≥3 replicates per texture. Controlled variable (1 pt): Soil column height, volume of water applied, degree of compaction, and ambient temperature must all be held constant across treatments to ensure differences in drainage are attributable only to texture.

Question 5: CRITICAL THINKING

A region receives 80 cm of annual precipitation. Agricultural fields in the region have soil with a porosity of 45% and a field capacity (water content after gravitational drainage) of 30% by volume. The root zone extends to a depth of 1.0 m. (a) Calculate the volume of water per hectare that the root zone can hold at field capacity. (b) If 40% of annual precipitation runs off or evaporates before entering the soil, calculate the depth of water that actually infiltrates per year. (c) Using your answers, explain whether this soil's water-holding capacity is likely sufficient for crop production during a 3-month dry season without irrigation. Justify your reasoning with a calculation.
Show answer
Part (a) (1 pt): Volume at field capacity = field capacity × depth × area = 0.30 × 1.0 m × 10,000 m² = 3,000 m³ per hectare. This is equivalent to 300 mm of water stored in the root zone. Part (b) (1 pt): Effective infiltration = 80 cm × (1 − 0.40) = 80 cm × 0.60 = 48 cm (0.48 m) per year. Part (c) (2 pts + 1 pt units): A typical crop requires approximately 4–6 mm of water per day during the growing season. Using 5 mm/day: demand over 90 days = 5 mm/day × 90 days = 450 mm = 0.45 m. The root zone at field capacity holds only 300 mm, creating a deficit of 450 − 300 = 150 mm. Therefore, the soil's water-holding capacity alone is insufficient to sustain crops through a 3-month dry season without supplemental irrigation or moisture-conserving practices (mulching, drought-tolerant varieties). Note: if porosity is 45% but field capacity is only 30%, the remaining 15% by volume drains under gravity, further confirming that not all stored water is plant-available.

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