1  Introduction

1.1 Evolution of New Zealand soils

The New Zealand Soil Classification broadly traces the evolution, or genesis, of New Zealand soils through time (Hewitt 1998). Figure 1.1 shows major pathways in the evolution of New Zealand soils. The pathways represent only those likely to have occurred over extensive areas, with many minor pathways or interlinkages omitted for clarity. In mineral parent materials, Raw Soils develop mostly into Recent Soils. The nature of the parent material then strongly determines the subsequent soil genesis pathway. Later, parent material becomes less important, and climate and vegetation, along with time, become more important controls over the character of the soil that evolves (Hewitt 1998; Hewitt et al. 2021).

In terms of soil order frequency in New Zealand, Brown Soils are most common (43%), followed by Podzol (13%), Pallic (12%), Pumice (7%), Recent (6%) and Allophanic (5%). The other nine orders account for the remaining 14% with Oxidic and Anthropic the least common with <1% each.

Soil formation, in its traditionally recognised form, proceeds by modifying a pre-existing parent material according to soil forming factors that dictate a range of processes and their impacts (Simonson 1959). In this situation, the soil profile originates via two steps: step 1, accumulation (or exhumation) of a fresh parent material at the land surface, followed by step 2, the modification of the parent material by soil-forming processes and weathering to form soil horizons leading to a deepening of the soil profile. However, the outcomes of this classical model of ‘topdown pedogenesis’ are modified when geological deposits (e.g., alluvium, tephra, loess, colluvium) are simultaneously added to the surface as it is commonly the case in New Zealand landscapes. Here, step 1 and step 2 occur together (not sequentially) so that the soil profile deepens as the land surface rises over time. This situation, when topdown pedogenesis occurs concomitantly with surface deposition, is called ‘upbuilding pedogenesis’ (Johnson et al. 1990). The concept of upbuilding pedogenesis was recognised in New Zealand more than 90 years ago (Taylor 1933), but it is only in comparatively recent times that it has become more fully appreciated. The deposition at the surface may be incremental (developmental upbuilding pedogenesis) or may comprise the sudden deposition of a relatively thick deposit that buries and isolates the antecedent soil (retardant upbuilding pedogenesis) (Hartemink et al. 2020; Palmer et al. 2025). Upbuilding pedogenesis is captured in the New Zealand Soil Classification mainly through the recognition of lithologic discontinuities and buried horizons (paleosols) in soil profiles, which demand specific notations (Clayden and Hewitt 2015) often indicated in the text by the term ‘buried’ (e.g., Buried-allophanic Orthic Pumice Soil). Upbuilding pedogenesis is predominant to common in Allophanic, Pumice, Pallic, Raw, Recent, Gley, Podzol and Brown soils, and various other soils also exhibit upbuilding pedogenesis to some degree (Hewitt et al. 2021).

1.2 The history of the New Zealand Soil Classification

The 4th edition of the Zealand Soil Classification is the culmination of a period of development from its initiation in 1983 to wide circulation of preliminary draft versions 1.0 and 2.0 (Hewitt 1987a; Hewitt 1989) for comment and testing before the revised version 3.0 (Hewitt 2010) was formally published in 1992 (Hewitt 1992a), reviewed by (Lowe 1992). The latest edition represents the best attempt, given the current state of knowledge, to classify New Zealand soils. As the knowledge and understanding of New Zealand soils grows, further revisions will be necessary.

The New Zealand Soil Classification is a national three-tier soil classification that replaced the New Zealand Genetic Soil Classification (Soil Bureau Staff 1948; Taylor and Cox 1957; Taylor and Pohlen 1962a; Taylor and Pohlen 1968)1. The New Zealand Genetic Soil Classification grew out of the need for reconnaissance mapping of the nation’s soil resources. It was successful as a unifying factor in New Zealand soil science, and it played a vital role in the development of pastoral agriculture. However, modern soil surveys and land evaluations required precise definition of classes and keys for their recognition. Furthermore, a new synthesis was needed of the large body of information collected since the 1950s (Hewitt 1992b). The first edition developed from the New Zealand Genetic Soil Classification and preserved various parts of it. Since then, the New Zealand Soil Classification has further evolved through experience in using the earlier editions and new knowledge. It has also been influenced by experience in testing the first edition of Soil Taxonomy (Leamy et al. 1983; Leamy et al. 1990; Hewitt 1992b), and the development of subsequent versions of Soil Taxonomy including the most recent edition and keys (Soil Survey Staff 1999; Soil Survey Staff 2022). With the 4th edition we also introduce an extended appendix that now includes an additional soil order (i.e., the Cryic Soil Order) and associated diagnostic criteria. This is to accommodate the soils of the Ross Sea Region of Antarctica, a focal point of Antarctic soil research with leading contributions of New Zealand soil scientists. It addresses the anomaly of New Zealand workers having to use international classifications when working in Antarctica. If, in the future, more empirical evidence emerges that taxa of the Cryic Soil Order might also be applicable to New Zealand soil environments (e.g., alpine environments of the Southern Alps), it can be shifted to the top of the main soil order key.

1.3 Objectives

The objectives of the New Zealand Soil Classification are:

  1. to provide a better means of communication about New Zealand soils and their utilisation;
  2. to provide an efficient vehicle for soil identification, recognition of soil families and series (4th and 5th level of the soil classification), correlation of previously defined soil series, and soil map legend establishment in soil surveys;
  3. to enable an efficient stratification of soil database information;
  4. to draw together knowledge of the properties of New Zealand soils and important similarities and differences among them.

A discussion of these objectives is given by Hewitt (1984); Hewitt (1987b) and the methods and rationale of the classification are provided by (Hewitt 1993).

1.4 Principles

To accomplish the objectives, the following principles have guided the development of this proposal. These are explained further by Hewitt (1984).

  1. The classification should be hierarchical, providing ascending levels of generalisation.
  2. The grouping of soils into classes should be based on similarity of measurable soil properties rather than presumed genesis.
  3. Classes must be designed to allow the greatest number and most precise accessory statements to be made about them consistent with their level in the hierarchy.
  4. Differentia should be based on soil properties that can be reproducibly and precisely measured or observed.
  5. Differentia should where possible allow field assignment of soils to classes, either directly, or by tested inferences.
  6. The nomenclature of higher categories should be based where possible on connotative English words chosen for their acceptability to nonspecialists.
  7. Where possible, continuity with successful parts of the New Zealand Genetic Classification should be maintained.
  8. The soil classification must be valid for the main islands of New Zealand. Classes must be correlated with Soil Taxonomy (Soil Survey Staff 1999; Soil Survey Staff 2022) to support international extension.

1.5 The soil individual

The soil individual is the fundamental unit of soil which is assigned to classes. Cline (1949) defined an individual as “the smallest natural body that can be defined as a thing complete in itself”.

Soil Taxonomy (Soil Survey Staff 1999) regards the polypedon as the soil individual. This is rejected here because, as discussed by Hewitt (1982), it does not fulfil the requirements for a soil individual by Cline (1949) or Johnson (1963). In New Zealand, the soil individual has traditionally been the soil profile. Usually conceived as a two-dimensional section exposed by a soil pit, it is in fact a three-dimensional slice sufficiently thick to sample and examine hand specimens. It should therefore be termed a “soil profile slice”. With the realisation that soils should be examined in successive horizontal sections as well as the vertical profile, there is increasing acceptance that a volume of soil the size of the pedon Soil Survey Staff (1999) represents a better soil individual than the soil profile slice.

Accordingly, the pedon as defined in Soil Taxonomy (Soil Survey Staff 1975) and referred to as “a unit of sampling” by (Soil Survey Staff 1999) is recommended as the soil individual for the New Zealand Soil Classification. It is understood that assignments are often made from the examination of volumes of soil smaller than a complete pedon, where they are assumed representative of the pedon. Notwithstanding this definition, it is noted that an alternative concept of the pedon was proposed by Holmgren (1988), this concept now forming in part the basis for digital soil mapping and thus also applying to parts of New Zealand’s soil survey online database, S-map: “A pedon is the possibility for soil observation in respect to a geographic point location. It can be realized by a set of observational propositions, each spatially and temporally specified in relation to that location”.

1.6 How to assign a soil to Subgroup level

Normally, a soil pit must be dug of sufficient size to expose the soil horizons to about 1 m depth, or to rock if shallower.

The soil horizons are examined and the assignment is then made by following the key, starting with the Key to Orders. The “Diagnostic Horizons and Other Differentiae” section is consulted as necessary to identify diagnostic horizons and other differentia, which will be applied according to a specified control section. For some classes, pH or other chemical measurements must be made. The characteristics of the soil are compared with the key statements of each soil order, starting with Organic Soils and passing down the key to the first soil order that fits them. When a soil order is identified, the chapter concerning that order is consulted and the keys to soil groups and soil subgroups are followed in the same manner to identify the appropriate soil group and subgroup. Note that in the keys to the groups and subgroups, the soils, following usage in Soil Taxonomy, are generally listed from more to least problematic in terms of most agricultural or horticultural land uses. For example, in Allophanic Soils, Perch-gley Allophanic Soils are listed first in the group keys, and Ironstone Perch-gley Allophanic Soils head the list in the subgroup keys, with subsequent taxa in each section having decreasing limitations for agriculture. Further, the word ‘typic’ does not necessarily mean the most extensive or typical; rather, it is a taxon representing soils without any of the characteristics defined for other taxa in the same class, (i.e., with no aberrant properties). Being placed last in the keys, it is in effect a default class. Similarly, the word ‘orthic’, meaning normal, conventional, represents a soil with no special qualities worthy of separate taxon status. It is not necessarily the most common taxon.

The name given to a soil assigned to a subgroup is made up of three elements in the sequence: subgroup, group, and order (for example, Nodular Perch-gley Oxidic Soils). Note that “Perch-gley”, being hyphenated, is one word, thereby conforming to these nomenclatural rules. Figure 1.2 illustrates the relationships between subgroups and groups in the Oxidic Soils order.

1.7 Soil series, families and siblings

It is possible to classify soils to a more detailed level than the subgroup. Historically, these were called soil series and originally constituted a grouping of soils with similar modal profiles, similar temperature and moisture regimes and the same or very similar parent materials and associated landforms (Taylor and Pohlen 1979). Consequently, soils in a series would usually behave in a similar way for land management. Identified by a geographical name, various subdivisions of a series including soil type (used commonly as a map unit) would carry the same name. Later this definition changed slightly, and soil series were defined according to three main criteria: the nature of the parent material or substrate, particle-size characteristics and the permeability profile (Hewitt 1992b). Because series were primarily used to describe natural soil-landscape units, the within-series variability could be significant and encompass soil properties including texture, stoniness, and depth to bedrock (Taylor and Pohlen 1979). As a result, pedons that traditionally belonged to the same soil series may today be classified into different subgroups. The formal definition and correlation of new soil series ceased in the early 1990s, but the existing series are still widely known and used by scientists, administrators and land users. Since then, soil series have been superseded by soil families. These are primarily used within the context of New Zealand’s soil survey database, S-map, and follow stricter classification rules based on the soil pedon characteristics than it was the case for soil series. A 5th level, the soil sibling (roughly equivalent to soil type), was introduced to further refine the description of the physical attributes within a family. Together, soil family and sibling are the soil entity (i.e., map unit) depicted in S-map. The definition and criteria of the 4th and 5th levels of soil classification are described in detail by Webb and Lilburne (2011).

1.8 Misclassification

The classes are the most important part of the soil classification. The key is merely a means of allocating soils to these classes, and by its nature is imperfect because only a sample of all the possible soils that might potentially be allocated were used in developing the key. Consequently, soils will be found that are not allocated to the appropriate class by the key. This will be apparent when a soil, allocated to a class, does not conform to the concept and accessory statements that can normally be made about that class. Because the key is the servant of the classes, the allocator is justified in placing the soil misfit into a more appropriate class. If this is done, however, it must be registered with the person with responsibility for the national soil classification system, so that appropriate adjustments may be made to the key when the soil classification is next revised. An allocation contrary to the key must also be noted in any records or publication of the allocation.

1.9 Justification of new subgroups

Justification for new subgroups may be made in two ways. First, if a soil is judged to be misclassified, and a more appropriate class is not available, then a new subgroup may be justifiable. Second, an existing subgroup may encompass a set of soils with properties that are too wide in range. The old subgroup could be split into two new ones. Splitting may be justified if it will significantly increase the number and precision of accessory statements that can be made about both of the new classes.

1.10 Correlations with other soil classification systems

Classes of the New Zealand Soil Classification do not correspond precisely with classes of other soil classification systems. Despite this, correlations can be made where classes are substantially equivalent. It is likely that all orders of Soil Taxonomy are represented in New Zealand, albeit some uncommonly or rarely, although Gelisols have not yet been formally identified Table 1.1.

Table 1.2 summarises the correlations of classes of the New Zealand Soil Classification with those of the New Zealand Genetic Soil Classification (Taylor and Pohlen 1968) and Soil Taxonomy (Soil Survey Staff 1999; Soil Survey Staff 2022). Further correlation with World Reference Base (IUSS Working Group WRB 2022) are presented in Hewitt et al. (2021).

Table 1.1: Areal representation (%) of soil orders in New Zealand based on Soil Taxonomy (from Hewitt et al. (2021))
Very common Common Less common Rare
Inceptisols (47.4) Alfisols (9.9) Mollisols (1.2) Oxisols (0.2)
Spodosols (13.1) Entosols (7.4) Histosols (0.9) Vertisols (0.1)
Andisols (12.9) Ultisols (4.2) Aridisols (0.9) Gelisols (<0.1)1
1 Small areas of Gelisols, underlain by contemporary permafrost in debris-mantled slopes, may occur in proximity to glaciers and rock glaciers above ~2000 m elevation in alpine areas of the South Island. Support for such occurrences is provided by the topoclimate modelling (Sattler et al. 2016) and abundant geomorphological evidence (e.g., Soons and Price (1990)), but actual ‘cryic’ soil profiles are yet to be observed. The Gelisols, provisionally represented as ‘Cryic Raw Soils’ in the New Zealand Soil Classification, therefore require further evaluation.
Table 1.2: Correlation of soil groups with the Genetic New Zealand Soil Classification (Taylor and Pohlen 1962b) and the US Soil Taxonomy (Soil Survey Staff 1999). The correlations with Soil Taxonomy provide only the nearest equivalents, as criteria differ between the two systems. The lowest category of Soil Taxonomy is given (order, suborder or great group) that can be best related to soil groups of the NZ Soil Classification.
NZ Soil Classification (v. 3) NZ Genetic Soil Classification US Soil Taxonomy
ALLOPHANIC SOILS
Perch-Gley Allophanic Soils gley soils Aquands
Gley Allophanic Soils gley soils Aquands
Impeded Allophanic Soils YB loams Cryands and Udands
Orthic Allophanic Soils YB loams Cryands and Udands
ANTHROPIC SOILS
Truncated Anthropic Soils anthropic soils Arents
Refuse Anthropic Soils anthropic soils Arents or Unclassified
Mixed Anthropic Soils anthropic soils Arents
Fill Anthropic Soils anthropic soils Arents
BROWN SOILS
Allophanic Brown Soils YB earths (upland & high country) Dystrochrepts
Sandy Brown Soils YB sands Ustochrepts, Dystrochrepts and Psamments
Oxidic Brown Soils YB earths (northern Dsytrochrepts
Mafic Brown Soils BG loams and clays Dsytrochrepts
Acid Brown Soils podzolized YB earthsor YB earths Dsytrochrepts
Firm Brown Soils YB earths, YB shallow and stony soils Dystrochrepts and Ustochrepts
Orthic Brown Soils YB earths, YB shallow and stony soils Dystrochrepts and Ustochrepts
GLEY SOILS
Sulpuric Gley Soils gley soils Sulphaquepts
Sandy Gley Soils gley soils Aquepts or Aquents
Acid Gley Soils gley soils Aquepts
Oxidic Gley Soils gley soils Aquox
Recent Gley Soils gleyed recent soils Aquents
Orthic Gley Soils gleyed recent soils Aquepts or Aquents
GRANULAR SOILS
Perch-gley Granular Soils BG loams or BG clays Aquults
Melanic Granular Soils BG loams or BG clays Humults and Udalfs
Oxidic Granular Soils BG loams or BG clays Humults
Orthic Granular Soils BG loams or BG clays Humults
MELANIC SOILS
Vertic Melanic Soils BG loams and clays Ustolls or Vertisols
Perch-gley Melanic Soils gley soils Aquolls
Rendzic Melanic Soils rendzinas Rendolls
Mafic Melanic Soils BG loams and clays Ustochrepts, Eutrochrepts, Ustolls or Udolls
Orthic Melanic Soils rendzinas and rendzinic intergrades Ustolls, Udolls or Eutrochrepts
ORGANIC SOILS
Litter Organic Soils unclassified Folists or unrecognised
Fibric Organic Soils organic soils Fibrists
Mesic Organic Soils organic soils Hemists
Humic Organic Soils organic soils Saprists
OXIDIC SOILS
Perch-gley Oxidic Soils gley soils Aquox
Nodular Oxidic Soils strongly weathered red loams, brown loams, or BG loams or BG clays Udox
Orthic Oxidic Soils strongly weathered red loams, brown loams, or BG loams or BG clays Udox
PALLIC SOILS
Perch-gley Pallic Soils yellow-grey earths Aquepts, Aqualfs
Duric Pallic Soils yellow-grey earths Duraqualfs
Fragic Pallic Soils yellow-grey earths Fragiudalfs, Fragiochrepts
Laminar Pallic Soils yellow-grey earths Haplustalfs, Hapludalfs
Argillic Pallic Soils yellow-grey earths Haplustalfs, Hapludalfs
Immature Pallic Soils yellow-grey earths or recent soils Eutrochrepts, Ustochrepts
PODZOLS
Densipan Podzols podzols Aquods, Orthods
Perch-gley Podzols gley podzols Aquods
Groundwater-gley Podzols gley podzols Aquods
Pan Podzols podzols Orthods
Orthic Podzols podzols Orthods
PUMICE SOILS
Perch-gley Pumice Soils gley soils Vitraquands
Impeded Pumice Soils YB pumice soils Vitrands, Vitricryands
Orthic Pumice Soils YB pumice soils Vitrands, Vitricryands
RAW SOILS
Gley Raw Soils unclassified Entisols, or not-soil
Hydrothermal Raw Soils hydrothermal soils Entisols, or not-soil
Rocky Raw Soils unclassified Entisols, or not-soil
Sandy Raw Soils unclassified Entisols, or not-soil
Fluvial Raw Soils unclassified Entisols, or not-soil
Tephric Raw Soils unclassified Entisols, or not-soil
Orthic Raw Soils unclassified Entisols, or not-soil
RECENT SOILS
Hydrothermal Recent Soils recent soils Aquents, Orthents
Rocky Recent Soils lithosols Orthents
Sandy Recent Soils recent soils Psamments
Fluvial Recent Soils recent soils Fluvents, Ochrepts
Tephric Recent Soils recent soils Orthents, Cryands, Udands
Orthic Recent Soils recent soils Orthents, Ochrepts
SEMIARID SOILS
Aged-argillic Semiarid Soils brown-grey earths Haplargids
Solonetzic Semiarid Soils solonetz Natragids
Argillic Semiarid Soils brown-grey earths Haplargids,
Immature Semiarid Soils brown-grey earths Camborthids
ULTIC SOILS
Densipan Ultic Soils YB earths or podzols Aquults
Albic Ultic Soils YB earths Aquults, Humults or Udults
Perch-gley Ultic Soils YB earths Aquults
Sandy Ultic Soils YB earths or YB sands Hapludults
Yellow Ultic Soils YB earths Hapludults

  1. Note that Soil Bureau Bulletin 3, entitled “A genetic classification of New Zealand soils”, was never published, except for the map “Soil map of New Zealand” in 1948.↩︎