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Podzols, also known as podosols, spodosols, or espodossolos, are the typical soils of coniferous or boreal forests and also the typical soils of eucalypt forests and heathlands in southern Australia. In Western Europe, podzols develop on heathland, which is often a construct of human interference through grazing and burning. In some British moorlands with podzolic soils, cambisols are preserved under Bronze Age barrows.[2]

Key Information

Term

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Podzol means "under-ash" and is derived from the Russian под (pod) + зола́ (zola); the full form is подзо́листая по́чва (podzolistaya pochva), meaning "under-ashed soil". The term was first given in mid-1875 by Vasily Dokuchaev,[3][4] and over time adopted by soil science. It refers to the common experience of Russian peasants of plowing up an apparent under-layer of ash (leached or E horizon) during first plowing of a virgin soil of that type.[5]

Characteristics

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Podzols can occur on almost any parent material but generally derive from either quartz-rich sands and sandstone or sedimentary debris from magmatic rocks, provided there is high precipitation.[6] Most Podzols are poor soils for agriculture due to the sandy portion, resulting in a low level of moisture and nutrients. Some are sandy and excessively drained. Others have shallow rooting zones and poor drainage due to subsoil cementation. A low pH further compounds issues, along with phosphate deficiencies and aluminum toxicity. The best agricultural use of Podzols is for grazing, although well-drained loamy types can be very productive for crops if lime and fertilizer are used.

The E horizon (or Ae in Canadian soil classification system), which is usually 4 to 8 centimetres (1.6 to 3.1 in) thick, is low in Fe and Al oxides and humus. It is formed under moist, cool and acidic conditions, especially where the parent material, such as granite or sandstone, is rich in quartz. It is found under a layer of organic material in the process of decomposition, which is usually 5 to 10 centimetres (2.0 to 3.9 in) thick. In the middle, there is often a thin horizon of 0.5 to 1 centimetre (0.2 to 0.4 in). The bleached soil horizon, which always has a higher value than the horizons above and below it, goes over into a red or red-brown horizon (so-called Podzolic B). The colour is strongest in the upper part, and change at a depth of 50 to 100 centimetres (20 to 40 in) progressively to the part of the soil that is mainly not affected by processes; that is the parent material. The soil profiles are designated by the letters A (topsoil), E (eluviated soil), B (subsoil) and C (parent material).

In some Podzols, the E horizon is absent—either masked by biological activity or obliterated by disturbance. Podzols with little or no E horizon development are often classified as brown Podzolic soils, also called Umbrisols or Umbrepts.

Geographic distribution

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Distribution of Podzol soils according to the World Reference Base for Soil Resources classification:
  Dominant (more than 50% of soil cover)
  Codominant (25–50%)
  Associated (5–25%)
The biome typically associated with Spodosols is coniferous forest.
Spodosols of the world

Podzols cover about 4,850,000 square kilometres (1,870,000 sq mi) worldwide and are usually found under sclerophyllous woody vegetation. By extent Podzols are most common in temperate and boreal zones of the Northern Hemisphere but they can also be found in other settings including both temperate rainforests and tropical areas.[7]

In South America Podzols occur beneath Nothofagus betuloides forests in Tierra del Fuego.[8]

Podzolization

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A Podzol with a characteristic eluvial (bleached, ash-colored) horizon and intensely coloured illuvial horizons. The photo was taken in the Feldberg area, Southern Black Forest, Germany.

Podzolization (or Podsolization[9]) is a complex soil formation process by which dissolved organic matter and ions of iron and aluminium, released through weathering of various minerals, form organo-mineral complexes (chelates) and are moved from the upper parts of the soil profile and deposit in the deeper parts of soil. Through this process, the eluvial horizon becomes bleached and of ash-grey colour. The complexes move with percolating water further down to illuviated horizons which are commonly coloured brown, red or black as they accumulate and consist of cemented sesquioxides and/or organic compounds. The podzolization is a typical soil formation process in Podzols.[9][10]

Preconditions

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Podzolization usually occurs under forest or heath vegetation and is common in cool and humid climates as these climates inhibit the activity of soil microbes in the topsoil. Overall, podzolization happens where the decomposition of organic matter is inhibited and as a result, acidic organic surface (mor) layers build up. Under these typically acidic conditions, nutrient deficiency further hampers the microbial degradation of organic complexing agents.[10][11] Medium to coarse textured soils with base-poor parent material (usually rich in quartz) also promote podzolization, as they encourage percolating water flow.[11][12]

Key steps

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The soil-forming process of podzolization can be broken down into two main steps:

  1. Mobilization and translocation of organic matter, Fe and Al from the surface horizon, and
  2. Immobilization and stabilization of organic matter, Fe and Al into the subsoil.[11][13][14]
    Podzol A layers

In the topsoil of acidic soils, organic matter (mostly from plant litter, the humus layer and root exudates) together with Al- and Fe-ions, form organo-mineral complexes. These soluble chelates then relocate with percolating water from the A (or E horizon) to the B horizon. As a result of this, the E horizon (or Ae horizon in the Canadian system of soil classification) is left bleached and ash-grey in colour, while the B horizon becomes enriched with relocated organo-mineral complexes. The colour of B horizon is consequently red, brown or black, depending on the dominance of metal ions or organic matter. Usually, the boundary between the B and eluvial Ae (or E) horizon is very distinct, and sometimes a hardpan (or Ortstein[12]) can form, as the relocated Fe and Al and organic matter increase mineral particles, cementing them into this compacted layer.[10][11][12]

There are several reasons why these organo-mineral complexes immobilize in the B horizon: If during the eluviation process more Al- or Fe-ions bind to the organic compounds, the complex can flocculate as the solubility of it decreases with increasing metal to carbon ratio. Apart from that, a higher pH (or higher Ca content) in the lower soil horizons can result in the breakdown of metal-humus complexes. In the lower soil layers, the organic complexing agents can be degraded by functioning microorganisms. Already established complexes in the B horizon can act as a filter, as they adsorb the traveling complexes from the upper soil horizons. A decreased water conductivity due to higher clay content can also result in the early flocculation of organo-mineral complexes.[10][11]

The relocated substances can sometimes separate in the illuvial horizons. Then, organic substances are mostly enriched in the uppermost part of the illuvial horizon, whereas Fe- and Al-oxides are mostly found in the lower parts of the illuvial horizon.[10]

Podzolization also promotes the relocation of some nutrients (Cu, Fe, Mn, Mo and P) that sometimes brings them closer to plant roots.[10]

In different soil classification systems

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The definitions in different soil classification systems are quite different. Especially soils that show pronounced other soil-forming processes in addition to podzolization are handled in different ways. The following correlations refer to soils, which have undergone advanced podzolization but lack prominent other soil-forming processes.

The term Podzols is used in the World Reference Base for Soil Resources[15] (WRB) and in many national soil classification systems (in some of them, spelled Podsols).

See also

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References

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Further reading

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
A podzol, also known as a podzolic or spodosol, is a type of acidic, sandy soil characterized by distinct horizons formed through the podzolization process, featuring a light-colored eluvial (Ae or E) horizon depleted of iron, aluminum, and organic matter, overlain by an organic-rich surface layer and underlain by an illuvial B horizon enriched with these translocated materials. These soils are typically quartz-rich, highly acidic (pH often below 4), and develop in coarse-textured parent materials under cool, humid conditions with annual precipitation exceeding 700 mm. Podzolization, the key soil-forming process, involves the mobilization of iron (Fe), aluminum (Al), and organic compounds by acidic waters from decomposing coniferous litter, which leach downward and precipitate in the subsurface B horizon, creating visually striking layers such as a grayish Ae horizon and reddish-brown (Bf), dark organic-rich (Bh), or mixed (Bhf) B horizons. This process can occur vertically through percolating soil water or laterally along hillslopes via subsurface flow, leading to variations in horizon thickness and composition; for instance, laterally developed spodic horizons are often thicker but lower in Fe and carbon content compared to vertically formed ones. Podzols may also feature cemented subsurface layers like ortstein (Fe-rich) or placic (Fe-impregnated) pans, which can impede drainage and root growth. These soils are predominantly associated with coniferous or boreal forests and heathlands, where acidic from vegetation such as pines, spruces, and ericaceous shrubs promotes the necessary chemical conditions for podzolization, though they can form under mixed forests in temperate humid climates. Formation typically requires base-poor, sandy or loamy parent materials derived from igneous rocks or glacial deposits, and the process can take from 40 to over 5,000 years depending on climate, vegetation, and . Globally, podzols cover approximately 485 million hectares, with the largest extents in boreal regions of (especially the Canadian Shield and ), , , and high-elevation mountains, as well as in wetter coastal areas like (with 1,500–3,000 mm ) and some tropical humid zones. In , they are classified into great groups like Humo-Ferric (Fe-dominant in drier conditions), Humic (organic-dominant in wetter areas), and Ferro-Humic (balanced), reflecting variations in B horizon chemistry and . Due to their low fertility and poor agricultural potential from nutrient leaching and acidity, podzols are often managed for , with challenges in cultivation unless limed and fertilized.

Introduction and Terminology

Definition

A podzol is a defined by the presence of a spodic horizon within 200 cm of the surface, typically underlying an albic, histic, umbric, or ochric horizon, or a thin anthropedogenic layer less than 50 cm thick. This spodic horizon represents an illuvial accumulation of amorphous materials, including complexed with aluminum and often iron oxides, distinguishing podzols as a reference soil group in the World Reference Base for Soil Resources. In the USDA Soil Taxonomy, the equivalent order is Spodosol, characterized similarly by a subsurface spodic horizon formed through the translocation of these substances. Unlike many other soil types, podzols develop through the process of podzolization, involving the leaching of soluble , iron, and aluminum from upper horizons in acidic, humid environments, resulting in a bleached subsurface layer. This translocation creates a distinct eluvial E horizon (often albic), which appears ash-like due to the removal of these compounds, setting podzols apart from soils like Ferralsols that retain high iron and aluminum concentrations without such leaching. Typically, a podzol profile features a surface organic layer () 1-5 cm thick, overlying a pale, E horizon that may extend 20 cm or more, followed by a reddish-brown to black Bs or Bhs spodic horizon enriched with the translocated materials. The spodic horizon usually forms within the upper 1 m of the , giving the profile a layered appearance of light gray over dark accumulation zones.

Etymology and Historical Usage

The term "podzol" originates from the Russian words pod (meaning "under" or "underneath") and zola (meaning "ash"), translating to "under-ash" and alluding to the pale, ash-like appearance of the leached subsurface horizon in these soils. This nomenclature was coined by the pioneering Russian soil scientist around 1879 during his foundational studies on soil genesis and classification in northern forested regions of . Dokuchaev's work emphasized the morphological features of soils, drawing from local observations to name types based on their distinctive profiles, marking a shift toward zonality in . In 19th-century Russian soil , "podzol" gained early recognition as part of Dokuchaev's innovative system, which integrated , , and to explain ; his expeditions and publications, such as those in the , highlighted podzols as typical of humid, coniferous environments. By the early , the term had been adopted in Western scientific literature, reflecting growing international interest in Russian ; the first documented English usage appeared in 1908, facilitating its integration into European and North American soil studies. Terminological variations emerged to describe similar soils across contexts and languages, including "podzolic soil" as an adjectival form denoting soils undergoing podzolization processes, and "Spodosol" in the U.S. Soil Taxonomy system, derived from Greek spodos ("") combined with Latin solum (""). In non-English languages, adaptations include "Podsol" in German, "Podsole" in Austrian classifications, "Podosol" in Australian systems, and retention of "Podzol" in French and nomenclature, accommodating regional phonetic and taxonomic preferences while preserving the core reference to the ash-gray horizon.

Soil Profile and Characteristics

Horizon Structure

Podzols exhibit a characteristic vertical layering of soil horizons that reflects the intense leaching and accumulation processes inherent to their formation. The typical sequence begins with an O horizon, consisting of undecomposed or partially decomposed organic litter from forest vegetation, often 1-5 cm thick and loose in texture. This is underlain by an A or Ah horizon, a dark layer of humified organic matter mixed with minerals, which serves as a transitional zone. Below this lies the E horizon, an eluvial layer where materials have been leached away, followed by the B horizon, an illuvial zone of accumulation, and finally the C horizon representing the unweathered parent material. Morphologically, the E horizon is distinctive for its ash-gray to white color and single-grain structure, resulting from the eluviation of clay, iron, aluminum, and organic compounds, giving it a bleached appearance that sharply contrasts with the overlying dark A horizon. The B horizon, often subdivided into Bs (sesquioxide accumulation) or Bhs (with additional ), appears reddish-brown to black and possesses a firm to massive structure, with subangular blocky peds in less cemented areas. In more advanced podzols, particularly those influenced by fluctuating water tables, the lower B subhorizons may develop cementation, forming ortstein—a hardened, indurated layer due to the binding of iron and aluminum oxides. The depth of the podzol profile varies with climatic conditions, typically ranging from 50-100 cm in colder boreal regions where development is limited by low temperatures and short growing seasons, while profiles in warmer temperate zones can extend deeper, often exceeding 100 cm, due to and translocation over longer periods. This horizon structure arises from the podzolization process, which drives the downward movement and redeposition of constituents.

Chemical and Physical Properties

Podzols exhibit high acidity, with typically ranging from 3.5 to 5.0, attributed to the accumulation of organic acids from decomposing coniferous and other . This low environment promotes intense leaching of base cations, resulting in low base saturation values often below 35% and correspondingly reduced (CEC), which averages around 5–10 cmol kg⁻¹ in subsurface horizons. The B horizon in podzols shows pronounced enrichment in amorphous aluminum (Al) and iron (Fe) oxides, as well as organic-Al and organic-Fe chelates, which form through complexation and translocation processes. These accumulations contribute to the soil's low fertility, characterized by deficiencies in phosphorus, which often becomes fixed as Fe/Al-phosphates, and calcium, due to ongoing leaching and low base cation retention. Physically, podzols commonly feature a sandy or loamy texture, with the E horizon displaying high permeability owing to its coarse, quartz-rich composition and low clay content (typically <10%). However, overall drainage is often poor, particularly in hydromorphic variants where cemented or dense illuviation layers in the B horizon restrict vertical water flow, leading to susceptibility to waterlogging and lateral seepage.

Podzolization Process

Environmental Preconditions

Podzols form primarily under cool and humid climatic conditions that favor intense leaching and minimal evaporation, with mean annual temperatures typically ranging from 5 to 15°C and annual precipitation exceeding 500 mm. These temperatures slow organic matter decomposition, allowing accumulation of acidic surface layers, while the high rainfall ensures excess water movement through the soil profile, enhancing the downward transport of solutes. Biotic factors play a key role, particularly the dominance of coniferous forests or heathlands, which produce litter rich in organic acids. For instance, pine needles and ericaceous shrubs generate low-pH humus (often below 4), releasing chelating agents like fulvic acids that mobilize aluminum and iron from upper horizons. This acidic organic input is essential for initiating the translocation processes characteristic of podzols. Geologically, podzols require coarse-textured parent materials low in weatherable minerals, such as quartz-rich sands, glacial till, or aeolian deposits derived from siliceous rocks like granite. These materials, often base-poor and highly permeable, permit rapid water percolation without retaining nutrients, thereby supporting the leaching regime necessary for podzol development.

Mechanisms and Stages

The podzolization process is driven by a series of interconnected chemical and biological mechanisms that facilitate the mobilization and translocation of elements within the soil profile. Central to this is the production of low-molecular-weight organic acids, such as citric, oxalic, and fulvic acids, generated through the microbial decomposition of plant litter and root exudates in the upper organic (O) and eluvial (E) horizons. These acids, primarily produced by fungi and bacteria, lower the soil pH, promoting acidification that enhances the solubility of aluminum (Al) and iron (Fe) oxides. The key mechanisms involve complexation, where organic acids form stable chelates with Al³⁺ and Fe³⁺ ions, rendering them mobile in soil solution, often as fulvic acid-metal complexes. This chelation is complemented by redox processes, particularly the reduction of Fe³⁺ to Fe²⁺ under periodically anaerobic conditions, which further increases Fe mobility before reoxidation and precipitation lower in the profile. These interactions lead to the formation of spodic materials—illuvial accumulations of organic matter, Al, and Fe—in the subsurface. Microbial activity, including ectomycorrhizal fungi and bacteria, plays a crucial role in accelerating acid production and complexation, influencing the rate of these processes. Podzolization unfolds in distinct stages over extended timescales, typically spanning 500 to 3,000 years or more, depending on environmental factors like moisture and vegetation. The first stage entails organic acid production and chelation in the upper horizons (O and A), where litter decomposition mobilizes Al, Fe, and dissolved organic matter (DOM). This is followed by eluviation, the downward percolation of these soluble complexes through the E horizon via infiltrating water, resulting in its bleaching due to depletion. In the third stage, illuviation occurs as the complexes reach the B horizon, where changes in pH, redox potential, or ionic strength cause precipitation and accumulation of organo-metallic compounds. Finally, ongoing precipitation and cementation in the B horizon solidify the spodic layer, with microbial mediation enhancing the efficiency of translocation throughout.

Distribution and Ecology

Global Occurrence

Podzols are most prevalent in boreal and subarctic regions of the Northern Hemisphere, where they dominate landscapes in Scandinavia, northwest Russia, Canada, and Alaska. In Scandinavia, particularly Sweden, podzols cover approximately 60% of the forest land area, spanning about 13.7 million hectares. In Russia, they occupy roughly 7% of the national territory, primarily in the northwestern and taiga zones. Canada features extensive podzols across 14.3% of its landmass, concentrated in eastern regions like northern Ontario, Quebec, and the Maritimes, as well as British Columbia and the Yukon. Globally, podzols encompass an estimated 485 million hectares, accounting for about 4% of the ice-free land surface, with over 80% occurring in boreal environments. Beyond the core boreal zones, they extend into temperate areas of northern Europe and occur in smaller but notable patches in New Zealand and high-altitude tropical regions, such as mountainous areas in South America and Southeast Asia. These distributions are largely driven by cool, humid climates that favor podzolization on coarse-textured, acidic parent materials. Regional variations in podzol development reflect differences in Quaternary history: in North America, many podzols formed on glacial till and outwash deposits from Pleistocene glaciations, leading to widespread occurrence on sandy, quartz-rich sediments. In contrast, European podzols, especially in Scandinavia and northern Germany, are often linked to periglacial processes in formerly unglaciated or ice-marginal areas, influencing soil texture and horizon development on aeolian and fluvial sands.

Associated Ecosystems and Environmental Role

Podzols are predominantly associated with boreal and temperate forest ecosystems, where they support vegetation adapted to nutrient-poor, acidic conditions. Dominant plant communities include coniferous forests dominated by species such as Norway spruce (Picea abies) and Scots pine (Pinus sylvestris), alongside ericaceous shrubs like heather (Calluna vulgaris) and bilberry (Vaccinium myrtillus) that form extensive understory layers. These plants rely heavily on symbiotic mycorrhizal associations—ectomycorrhizae for conifers and ericoid mycorrhizae for shrubs—to enhance nutrient uptake, particularly phosphorus and nitrogen, from the leached soils. Such adaptations enable persistence in environments with low fertility, where organic matter decomposition is slow due to cool temperatures and high acidity. Faunal communities in podzol ecosystems reflect the boreal habitat, supporting wildlife such as moose (Alces alces), lynx (Lynx canadensis), and snowshoe hares (Lepus americanus), which utilize the forested cover and understory for foraging and shelter. Soil fauna is limited, with scarce large invertebrates like earthworms due to acidity and aluminum toxicity; instead, decomposition is driven by fungi and small arthropods. Hydrologically, podzols contribute to water retention and filtration in forested catchments, regulating dissolved organic carbon (DOC) export to streams through riparian processes that buffer nutrient loads. However, their inherent acidity can lead to aluminum mobilization and acidification of runoff, potentially harming downstream aquatic life during high-flow events. In terms of environmental role, podzols excel in organic carbon sequestration, with the O horizon often storing substantial amounts—up to 25-50 t ha⁻¹—of slowly decomposing litter, stabilizing carbon in cool, moist conditions. This capacity positions them as significant sinks in boreal carbon cycles, though their vulnerability to climate warming is pronounced; elevated temperatures accelerate decomposition and permafrost thaw in Arctic regions, releasing stored carbon and exacerbating degradation. As of 2025, studies indicate that abrupt permafrost thaw can stimulate carbon release, potentially amplifying climate feedbacks in podzolic soils. Their infertile properties severely limit agricultural productivity, restricting use to low-intensity grazing rather than crops, without amendments. Conversely, podzols are vital for sustainable forestry, providing habitats for timber species like pine and spruce, where management practices enhance wood production while preserving ecosystem services.

Classification and Nomenclature

In Major Soil Taxonomies

In the United States Department of Agriculture (USDA) Soil Taxonomy, podzols are classified within the order Spodosols, which is defined by the presence of a spodic horizon characterized by illuvial accumulations of amorphous materials including aluminum and organic carbon, along with specified levels of extractable aluminum and iron. This order encompasses soils typically formed under acidic, humid conditions on coarse-textured parent materials, distinguishing Spodosols from other orders like Alfisols or Ultisols based on the dominance of these subsurface accumulations. The World Reference Base for Soil Resources (WRB), an international system developed under the International Union of Soil Sciences, designates these soils as the Reference Soil Group Podzols, requiring a spodic horizon with significant translocation of metal-humus complexes and low base saturation. Podzols in the WRB are further subdivided into qualifiers such as Humic (for those with high organic carbon in the subsurface horizon) or Albic (indicating a light-colored eluvial horizon), allowing for nuanced classification based on horizon properties and environmental influences. This framework emphasizes diagnostic horizons over strict pedogenic processes, facilitating global soil mapping and correlation. In the FAO/UNESCO Legend for the Soil Map of the World, podzols are recognized as a major soil group under the name Podzols, characterized by acidic conditions and pronounced leaching leading to a bleached A horizon overlying a dark B horizon enriched with organic matter and sesquioxides. This system, developed in the 1970s for large-scale global assessments, treats Podzols as a distinct grouping within 26 major soil units, highlighting their occurrence in cool, moist climates on siliceous sands. Historically, the Canadian System of Soil Classification includes podzols within the Podzolic order, which is one of ten orders and defined by the development of a podzolic B horizon through the translocation of organic matter and iron-aluminum compounds under forested, humid conditions. This order is subdivided into great groups such as Humo-Ferric Podzol, emphasizing variations in the ratio of organic carbon to iron in the illuvial horizon, and reflects Canada's focus on regional pedogenic features in boreal and temperate zones. These taxonomic approaches illustrate nomenclature variations, with "Spodosols" derived from the Greek for "ash-like" to denote the eluvial horizon, while "Podzols" retains the Russian term for "under-ash" soils.

Diagnostic Criteria and Variants

The diagnostic criteria for podzols emphasize the presence of distinct eluvial and illuvial horizons formed through podzolization, with specific morphological, chemical, and physical thresholds to ensure classification precision. In the World Reference Base for Soil Resources (WRB), podzols are identified by an overlying albic (E) horizon at least 1 cm thick exhibiting light colors (value ≥4 moist, chroma ≤2) and low base saturation (<50% by NH₄OAc at pH 7), underlain by a spodic (B) horizon with illuvial accumulations of organic matter, aluminum (Al), and iron (Fe). The spodic horizon must be at least 2.5 cm thick, contain >0.5% organic carbon, and meet chemical thresholds such as Al + ½Fe (extractable by ) >0.5%, demonstrating translocation from the overlying horizon. These criteria distinguish podzols from other acid soils by quantifying the degree of leaching and illuviation. In the , equivalent Spodosols require a spodic horizon within 200 cm of the surface, with similar thresholds: organic carbon ≥0.6% and Al + ½Fe ≥0.50% (-extractable), often accompanied by an optional albic horizon ≥1 cm thick showing eluviation of clays and Fe oxides. The base saturation in the spodic horizon or the 50 cm above it is typically ≤35%, reinforcing the acidic, leached nature. These measurement-based diagnostics, using field morphology and laboratory analyses like oxalate extraction, provide objective identification while accounting for variations in horizon continuity (≥50% of the pedon). Podzol variants are subclassified based on spodic horizon composition, cementation, and parent material influences, affecting classification in systems like the Canadian System of Soil Classification. The ortstein variant features a cemented Bhs or Bhf horizon (≥3 cm thick, with ≥50% indurated structure due to organic-Al-Fe complexes), forming in coarser-textured materials under prolonged saturation. Ferrohumic podzols exhibit Fe-rich spodic horizons (Bhf) with appreciable Fe oxides alongside humus, often in humid, well-drained settings on glacial till or sands. Humodur variants are organic-rich with cementation dominated by humus and Al (>5% organic carbon in the cemented layer), typically developing in siliceous parent materials like quartz sands. Parent material texture and mineralogy, such as high quartz content, enhance cementation in ortstein and humodur types by limiting base cations and promoting Al-organic bonding. Recent updates in the WRB 2022 edition allow for a cryic qualifier on Podzols in cold, non- environments. Soils with and spodic horizons are classified as Cryosols, refining the representation of high-latitude or alpine soils without altering core horizon criteria.

References

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