Open Access
How to translate text using browser tools
18 January 2022 Proposed changes to the soil family taxon within the Canadian System of Soil Classification
C. James Warren, Daniel D. Saurette
Author Affiliations +
Abstract

The soil family was developed in the 1960s as the fourth level of taxa within the hierarchical structure of the Canadian System of Soil Classification. The original aim of the soil family category was to provide a framework for checking and establishing limits for soil series while providing a link between the series and the subgroup level. Its intended use was to define and group numerous soil series based on soil characteristics important for the purpose of applying appropriate management practices. In the current Canadian System of Soil Classification, taxa at the family level represent subdivisions of the subgroups. Classification of mineral soils at the family level is based on properties of the parent materials which include particle size; soil mineralogy; reaction (soil pH); calcareousness; depth to bedrock and permafrost; as well as climactic factors: soil temperature and soil moisture regimes. The soil family particle-size classes were originally intended as a compromise between both agronomic and engineering influences; however, the resulting product has limited functionality because of differences in definitions between engineering and agronomic grain sizes and non-alignment with soil textural classes. Consequently, classification and use of the family taxon have largely been ignored. Some adjustments to the family taxon for mineral soils and terric layers in organic soils are proposed including realignment of classes in the current family particle-size triangle to follow the divisions of the soil textural classes. Minor adjustments to mineralogy classes and depth to bedrock are also proposed.

Introduction

The soil family occupies the fourth taxonomic level within the hierarchical structure of the Canadian System of Soil Classification (CSSC) below subgroups, great groups and orders and above the soil series which is the recommended primary mapping unit in soil maps ranging from survey intensity level 1 (very detailed) to 4 (broad reconnaissance; Coen 1987). The concept of the soil family was first introduced to soil classification in Canada in 1955 as a direct adoption of the family taxonomic level of US Soil Taxonomy at that time (NSSC 1955). It received a formal definition in the Canadian system in the 1963 version; however, pedologists and soil surveyors were solely focused on the three highest taxonomic levels (order, great group and subgroup) at the time (NSSC 1963). Further development of the soil family taxonomic level in the 1960s led to proposed criteria for family classification in 1965 to be used on an evaluation basis by provinces (NSSC 1965) and finally adoption of official terminology and class limits closely resembling those developed for the US Soil Taxonomy in 1968 and updated in 1973 (Broersma 1972; CSSC 1973; Michalyna 1972; NSSC 1968; SCWG 1998). The original aim of the family category was to provide a framework for checking and establishing limits for groups of soil series while providing a link between the series and the subgroup levels. The family category was needed to provide a means of grouping soil series to determine and apply appropriate management practices and was originally defined by Canadian pedologists as ‘a group of soil series that are relatively homogeneous with respect to soil-air, soil-water, and plant-root relationships’ (NSSC 1963). Inclusion of the family taxon was necessary because the number of individual soil series was far too great to develop management practices for each individual series, and the higher categories are too heterogeneous to be adapted for many management purposes. Even though the soil family provides a useful framework to group soils based on similar moisture, fertility, drainage, parent materials, etc. and has a high potential to group soils based on their characteristics important for crop growth, this taxonomic level remained largely undeveloped (NSSC 1965). Unfortunately, the family category was not adopted as readily as the other taxonomic levels, and as a consequence, application and use of the soil family category have largely been ignored (SCWG 1998).

In the third edition of the CSSC (SCWG 1998), ‘taxa at the family level are formed by subdividing subgroups’. Thus, families carry the differentiating criteria of the order, great group and subgroup to which they belong. Families within a subgroup are differentiated based on parent material characteristics, including particle size, mineralogy, calcareousness, reaction and depth and soil climatic factors (SCWG 1998). Soil family criteria differ between mineral and organic soils in the third edition of the CSSC manual (SCWG 1998). Genetic soil factors are adequately addressed at the order, great group and subgroup levels. The criteria for differentiation of soils at the family level generally relate to physical and chemical composition, thickness of the parent materials and climatic factors. Family criteria are applied uniformly across the mineral soil orders while the organic order is addressed separately. Differentiating criteria for mineral soils at the family level as outlined in the CSSC manual (SCWG 1998) are particle size (p. 136); mineralogy (p. 139); depth to lithic and cryic contacts, (p. 139); reaction (p. 139); calcareousness (p. 141); and soil climate (soil temperature regime; and soil moisture regime, p. 141). Differentiating criteria for organic soils at the family level are characteristics of the surface tier (p. 141); reaction (p. 141); soil climate (soil temperature regime and soil moisture regime (p. 141); particle size of any terric layer (p. 144); kind and depth of limnic layers (p. 144); and depth to lithic and (or) cryic contacts (p. 144). Particle-size classes for terric layers within organic profiles are the same as for mineral soils, but the criteria for depth to lithic and (or) cryic contact differ for mineral and organic soils. Discussion here will focus primarily on proposed changes to soil family particle-size classes including particle-size classes of terric layers in organic soils. Minor changes are also proposed to the mineralogy, reaction and calcareous class and depth classes primarily for completeness or to correct perceived omissions.

Review of Current Soil Family Taxon

Current soil family particle-size criteria

For the purposes of classification at the family level, as currently defined in the CSSC (SCWG 1998), particle size refers to the whole soil composition including coarse fragments (>2 mm diameter). Family particle size is related to soil texture but differs in that soil texture refers specifically to the composition of the fine earth fraction (i.e. proportion of sand, silt and clay size particles ≤2 mm diameter) and is specific to individual horizons. Family particle size includes the fine earth fraction by mass (≤2 mm diameter) plus coarse fragment (>2 mm diameter) content by volume averaged for the entire control section of the profile. Exceptions are provided for soils with strongly contrasting particle sizes within the control section that affect soil properties which are not captured at higher taxonomic levels (SCWG 1998, p. 138–139). Modifiers for coarse fragment content are applied to soil texture classes for each horizon, but these are not separate texture classes (Day 1983). In practice, family particle size is typically assessed based on the textures within a profile weighted for the thickness of each horizon plus consideration of the overall coarse fragment content.

Within the current version of the CSSC (SCWG 1998), there are 11 classes/categories used to describe particle-size characteristics at the family level. Note however that only seven classes are presented in the family particle-size triangle (Fig. 1; SCWG 1998, p. 136) because the remaining four classes result due to increased coarse fragment content. These are: clayey-skeletal (includes very fine clayey and fine clayey base classes with ≥35 to <90% coarse fragments by volume), loamy-skeletal (includes coarse-loamy, fine-loamy, coarse-silty and fine-silty classes with ≥35 to <90 % coarse fragments), sandy-skeletal (includes sandy class with ≥35 to <90% coarse fragments) and fragmental (soils composed of ≥90% coarse (>2 mm diameter) fragments). Versions of particle size prior to 1973 had only three primary particle size classes: coarse, medium and fine which followed boundaries to form groups of soil textural classes plus skeletal versions for each and a fragmental group (NSSC 1968). The classes, adopted from US Soil Taxonomy, were originally intended to reflect an equal balance between agronomic and engineering influences (CSSC 1973). For example, the limit of 18% clay between coarse-loamy and fine-loamy classes reflects the change from non-plastic to plastic behaviour with increasing clay content (Handy and Fenton 1977). This is considered by engineers to be an important distinction. Similar breaks related to plastic and liquid behaviour occur at 35% and 60% clay content. There is also a difference between the coarse and fine silty and loamy classes, which relate to capillary rise and available moisture-holding capacity. These breaks were intended to allow groupings of soils with similar responses to management and to some extent, for engineering and related uses (SCWG 1998).

Fig. 1.

Current particles-size classes (left) and soil textural classes (right) based on SCWG (1998).

cjss-2021-0146f1.tif

Impracticality of the current soil family particle-size classes

When comparing the current family particle-size classes with soil texture classes (Fig. 1), it quickly becomes evident that the boundaries between many of the family particle-size classes do not coincide with boundaries for textural classes, resulting in particle-size boundaries dividing soil texture classes. Exceptions are the breaks between clay and heavy clay textures corresponding to fine-clayey and very-fine-clayey particle sizes and the boundary between sandy and coarse-loamy particle-size classes coinciding with the boundary between sandy loam and loamy sand textures. There is also a difference between the engineering and agronomic definitions in the grain-size cutoff for sand and silt-sized particles where the cutoff for agronomic applications is typically 0.05 mm diameter while engineering applications use 0.074 mm (SSDS 2017; Schoeneberger et al. 2012). There are also differences between engineering and pedological definitions for subdivisions (fine, medium and coarse) of gravel (USDA 1987; Schoeneberger et al. 2012).

Although the current family particle-size classes were intended as a compromise to incorporate engineering criteria at the family level (CSSC 1973), different classification systems exist worldwide which are used for different applications (Garcia-Gaines and Frankenstein 2015), and sometimes there is no direct relationship between systems. Whereas pedologists are more concerned with the control section, engineers focus primarily on parent materials and materials below (Pawluk 1970). In fact, regulations require that topsoil (A horizon materials) must be stripped and stockpiled from sites prior to construction activities of interest to engineers. Engineering properties of the solum are consequently of little use in practice.

The utility of the current particle-size triangle was based on the premise that analytical data such as sand, silt and clay content (including values for the 0.074 mm division between sand and silt) and coarse fragment content were collected and readily available (i.e., published soil survey reports) in addition to agronomic attributes required for classification at the series level. Soil survey maps and reports are often lacking engineering test data such as Atterberg and plasticly indexes, particle-size distributions according to unified and or A.A.S.H.O. systems which are not commonly used by agronomists, and therefore these reports are of limited direct utility to engineers without additional interpretations or assumptions. Data required for particle-size classes are for the most part lacking and definitely absent in older soil survey reports before the advent of the soil family class. Grain-size distributions expressed as a graph also afford more useful information for engineers than do particle-size classes, and because such interpretations are multi-disciplinary, they should be handled separately (Pawluk 1970). Although there were some indifference and reluctance among soil survey committee members at the time to adopt family criteria, it was recognized that there was a need to sort and group soil series to point out discrepancies in the criteria used for soil series (CDA 1970).

Soil survey reports, with some exceptions, provide profile descriptions with soil texture classes for individual horizons with only some original data for grain-size analyses (percentages of sand, silt and clay). In Canada, some data related to engineering properties have been included in soil survey reports; however, they are often limited to single pedons for soil series with extensive areal distribution (e.g., Presant and Wicklund 1971; Coen and Holland 1976; Eilers and Halstead 1981; Luttmerding 1981; Wang and Rees 1983; Kingston and Presant 1989; Lamontagne et al. 2014) and are only available for a limited number of published soil surveys. Whereas textural classes see immediate use in classification at the series level, grouping of soil series into soil families for the purpose of applying management practices may only be considered sometime later. Any analytical data collected at the time of sampling may have been lost, or the original textural data may have been estimated from hand texturing. The result being that the current particle-size classes are difficult to accurately assess, particularly when based on older pedological data without additional data required for classification at the family level typically not collected initially. Consequently, the family classification has largely been ignored in the past, and agronomic management practices have been applied with little formalized guidance towards grouping of soils for targeting proposed management practices which was the original intent of the family taxon. Use of family classes to group soil series for application of appropriate management practices would have a benefit of streamlining and efficiently targeting field trials to help identify and target soils which may have been overlooked in the past or alternatively avoid duplication of research efforts on soils that are similar. This would also aid in identifying soils with similar properties at the family level for application of appropriate management practices targeting specific soils.

Another disadvantage of the current family classification is the use of long attribute-based family names, making their application very cumbersome. Although the attributes are highly descriptive, assignment of a common soil series name to designate each family has been recommended for convenience and brevity (SCWG 1998, p. 144). Adoption of a series name (e.g., Breton family in place of Orthic Gray Luvisol, fine-loamy, mixed, neutral, cold, subhumid family) for the family name based on a series that is most representative (i.e. greatest areal extent) or oldest or most recognized name within a given soil family class would be most appropriate. Formalized adoption of common series names in place of attribute-based names would help facilitate more widespread application and ease of use.

Proposed Revisions to the Soil Family Taxon

Particle-size classes

Proposed changes to soil particle-size classes are summarized in Figs. 2, 3 and 4. The modified ‘Base’ particle-size triangle (Fig. 2) is similar to s-type particle sizes used in Forest Ecosystem Classification (Sims et al. 1989) which align with soil texture (fine earth) classes. This triangle (Fig. 2) is proposed to replace the particle-size triangle on Figure 41, left side (p. 136) of CSSC (SCWG 1998). These new proposed particle-size classes are based on percentages by weight of clay, silt and sand using 0.05 mm (50 μm) as the division between sand and silt grain sizes. An exception is that very fine sand textures are lumped with the coarse-loamy particle class rather than the sandy particle-size class. Soils containing coarse fragments of all sizes >2 mm diameter exceeding 35% by volume (approximately 50% by mass) and classified as ‘skeletal’ are summarized in a new figure (Fig. 3), while those soils with ≥90% coarse fragments of all sizes >2 mm diameter by volume are classed as fragmental. Coarse fragments as defined within certain size and shape ranges are shown in Table 1 (Day 1983). To maintain consistency, the proposed particle-size class names and those for ‘skeletal’ and fragmental classes are the same as the current version of the CSSC (SCWG 1998), except that the boundaries have been shifted to coincide with soil texture boundaries (Fig. 3).

Fig. 2.

Proposed particle-size triangle for soils with <35% coarse fragments by volume. *Very fine sand is included with coarse-loamy particle-size class.

cjss-2021-0146f2.tif

Fig. 3.

Proposed particle-size triangle for soil with ≥35% to <90% coarse fragments by volume (i.e., skeletal soils). *Very fine sandy-skeletal is included with loamy-skeletal particle-size class.

cjss-2021-0146f3.tif

Fig. 4.

Proposed particle-size triangle describing terric layers within organic soils. *Very fine sand is included with the loamy particle-size class.

cjss-2021-0146f4.tif

Table 1.

Modifiers applied to texture classes based on coarse fragment (>2 mm diameter) shape and size.

cjss-2021-0146tab1.gif

Textural and engineering soil classification systems are not directly translatable because the latter are not based purely on texture (grain size) but also use plasticity data which is reflected in clay mineralogy. It is unlikely that a precise translation between textural and engineering classifications will ever be made because their purposes differ (Handy and Fenton 1977). Engineering classifications are directed towards variations in soil behaviour relevant to engineering, and textural classifications are more concerned with pedological description. Consequently, soil data required for engineering purposes should be collected and handled separately and in addition to pedological data.

The distinction between coarse-silty and fine-silty particle-size classes has been combined in favour of a larger single silty particle-size class that encompasses silt and silt loam textures. The distinction between coarse and fine silty particle-size classes relates to differences in support strength and to a lesser extent moisture-holding capacity (Handy and Fenton 1977). Although the occurrence of pure silty materials (coarse-silty particle size) may be more common in the United States, they seem to be rare in the Canadian landscape, thus not warranting more than a single particle-size class. This reduces the number of ‘base’ particle-size classes (coarse fragment contents <35% by volume) from 7 to 6. Similarly, proposed particle-size classes for soils with coarse fragment contents ≥35% by volume (Fig. 3) also have boundaries coinciding with soil texture boundaries retaining particle-size class names from the current version of the CSSC. A new silty-skeletal class is proposed, and although rare, it is included for completeness (Fig. 3). Figure 4 provides the particle-size classes used to described terric layers found in organic soils. All 10 proposed family particle-size classes are summarized in Table 2. Table 3 provides a summary of proposed family particle-size classes along with corresponding modifiers used for soil texture classes for horizon descriptions which are based on coarse fragment content by volume.

Table 2.

Summary of proposed soil family particle-size classes.

cjss-2021-0146tab2.gif

Table 3.

Summary of soil texture class modifiers and family particle-size classes based on coarse fragment content.

cjss-2021-0146tab3.gif

Classification of soils with two or more parent materials in the control section with strongly contrasting particle-size classes must also be revised. Table 4 provides a listing of terms for particle-size classes for soils having strongly contrasting layers. The difference from the prior table (SCWG 1998, p. 139) is the combination of coarse-silty and fine-silty particle size columns into a single silty class and addition of the silty-skeletal class. The minimum significant thickness of a strongly contrasting layer is 15 cm, and the transition between layers is less that 12 cm thick as per the current version (SCWG 1998). Table 4 herein should be substituted for table 1 on page 139 of the CSSC for consistency with the proposed changes.

Table 4.

Strongly contrasting particle sizes.

cjss-2021-0146tab4.gif

Mineralogy classes in mineral soils

A minor change/addition to table 2 Key to Mineralogy Classes (p. 140) of the current version of the CSSC (SCWG 1998) is to add a ‘Mixed’ class under ‘Classes applied to soil families of any particle-size class’ (SCWG 1998, p. 140, table 2). This class is proposed as a mixed mineralogy class which is by far the most common mineralogy class compared with those currently listed yet was not included in previous versions.

Reaction classes in mineral soils

Table 5 is proposed as an amendment to reaction classes for mineral soils substituting for the current listing of pH reaction classes on page 141 of the current version of the CSSC (SCWG 1998). The amended table adds the more detailed reaction classes as reported in Day (1983) to aid in clarity for the reader.

Table 5.

Soil family reaction classes and corresponding field pH ranges.

cjss-2021-0146tab5.gif

Calcareousness classes in mineral soils

A minor change to family calcareousness classes is the addition of a non-calcareous class corresponding to acid and neutral pH classes (Table 6). This additional calcareous class is proposed for completeness and to be substituted for the current list on page 141 in the current version of the CSSC (SCWG 1998).

Table 6.

Soil family calcareous classes and corresponding field calcareous class ranges.

cjss-2021-0146tab6.gif

Depth classes in mineral soils

Table 7 provides a comparison between current and proposed depth classes for lithic and permafrost (cryic) contacts for mineral soils. Proposed additions are the inclusion of non-lithic and non-cryic classes for soils with lithic contacts or permafrost contacts at >100 cm depth. These new criteria are proposed for completeness but may be omitted from many descriptions. There are no changes proposed for lithic and permafrost for organic soils. It is proposed that the depth of the lithic and cryic contacts between very shallow and extremely shallow be changed from <20 cm to <25 cm for consistency with other world soil classification systems and inclusion of the Leptosolic order to the CSSC (see Warren et al. In press). It is also proposed for the time being that the extremely shallow lithic criteria be applied as necessary only as a phase to very shallow lithic families. Otherwise, because of the hierarchical structure of the CSSC, assignment of separate series names would necessitate differentiation at the series level for soil belonging to extremely shallow vs. very shallow families. This is recommended in an effort to minimize unnecessary proliferation of soil series names.

Table 7.

Soil family depth classes for mineral soils (lithic and cryic).

cjss-2021-0146tab7.gif

All cryic criteria need only be applied in the case of extremely cold and very cold soil temperature regimes. Otherwise, a non-cryic class is implied and not explicitly used as it is redundant for all temperature regimes warmer than very cold and therefore omitted from most family class names.

Implications for acceptance of the proposed revisions

Adoption of the proposed family particle classes would align with particle-size classes which are currently used in Forest Ecosystem Classification (CFEC 2010) and other classification systems in Canada (Sims et al. 1989). Adoption of proposed particle-size criteria will also facilitate use of historical soil survey data published prior to the introduction of the soil family taxon in the 1960s for classification of these soils at the family level. This would facilitate a means of grouping soils with similar properties at the family level for application of appropriate management practices targeting specific soils which was the original intent of implementing the soil family taxon. Use of family classes to group soil series data for application of appropriate management practices would have a benefit of targeting field trials to develop management practices for soils which may have been overlooked in the past or alternatively avoid duplication of research efforts on soils with similar properties. The proposed changes will also separate engineering properties from pedological properties. Engineering data should be included in future soil survey reports; however, it should be collected and tabulated specific to engineering uses separate from pedological classification.

Recommendations

The following recommendations are based on the above discussion:

  1. Adopt the revised soil particle-size classes as outlined in Figs. 2, 3 and 4 and summarized in Table 2 to replace the current versions of the soil family particles-size classes in the CSSC (SCWG 1998). These proposed changes align the family soil particle-size classes with soil texture classes. Adoption of these modifications will facilitate broader adoption and utility of the soil family class through retro-classification based on soil series data from pre-1960 soil survey data as well as new and future pedological surveys. Substitute Table 4 herein for table 1 on p. 139 of the CSSC (SCWG 1998).

  2. Explicitly include ‘Mixed’ as a mineralogy class for all particle-size classes to facilitate clarity and completeness.

  3. Explicitly include ‘non-calcareous’ as a calcareousness class for acid and neutral pH reactions to facilitate clarity and completeness. Substitute Tables 5 and 6 herein for lists on p. 141 of the CSSC (SCWG 1998).

  4. Explicitly include ‘non-lithic’ as a depth to bedrock class for soils with lithic contacts >100 cm to facilitate clarity and completeness. Substitute Table 7 for the list on page 139 of the current CSSC (SCWG 1998).

  5. Substitute Table 1 herein for table 9 on page 157 of the CSSC (SCWG 1998).

  6. Add Table 3 herein to Chapter 17 of the CSSC (SCWG 1998, p. 157).

  7. Formalize the assignment of a ‘Family Name’ based on a series name within each family group to abbreviate the current attribute-based family descriptor names. The assigned family name should be based on the soil series name that is most representative (i.e. greatest areal extent) or oldest or most recognized series name within each given soil family class (e.g. Breton family).

References

1.

Broersma, C. 1972. Soil Families. Pages 213–217 IN Report on the Second Meeting of the Western Section of the Canada Soil Survey Committee. Kelowna, BC. Feb. 15–17, 1972, 217 pp. Google Scholar

2.

Canada Department of Agriculture (CDA). 1970. The system of soil classification for Canada. Queen's Printer for Canada, Ottawa, ON. 255 pp. Google Scholar

3.

Canadian Forest Ecosystem Classification System (CFEC). 2010. Baldwin, K. Natural Resources Canada. Canadian Forest Service. Great Lakes Forestry Centre, Sault Ste Marie, Ontario. Frontline Express 38. 2 p. Google Scholar

4.

Canadian Soil Survey Committee of Canada (CSSC). 1973. Report on the nineth meeting of the National Soil Survey Committee of Canada. University of Saskatchewan, Saskatoon, Saskatchewan. May 16–18, 1973, 358 pp. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1973_cssc_9thmeeting.pdf Google Scholar

5.

Coen, G.M. 1987. Soil survey handbook. Volume 1. Technical Bulletin 1987-9E. Land Resource Research Centre Contribution Number 85-30. Research Branch. Agriculture Canada, Ottawa, Ontario. 135 pp. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/manuals/1987-9/index.htmlGoogle Scholar

6.

Coen, G.M., and Holland, W.D. 1976. Soils of Walkerton lakes National Park, Alberta. agriculture Canada, research branch, soil research institute and environment Canada, Northern Forest research centre. Alberta Institute of Pedology, Edmonton, Alberta. S-73-33.Information report NOR-X-65. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/ab/ab33/ab33_report.pdfGoogle Scholar

7.

Day, J.H. (ed.) 1983. The Canada soil information system (CanSIS). Manual for describing soils in the field. 1982 Revised. Land Resource Research Institute, Ottawa, LRRI Contribution No. 82–52. Google Scholar

8.

Eilers, R.G., and Halstead, B.E. 1981. Soils of the Dauphin Area. Report D-34. Canada-Manitoba Soil Survey. Agriculture Canada. Manitoba Department of Agriculture. Department of Soil Science, University of Manitoba. Winnipeg, Manitoba. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/mb/mbd34/mbd34_report.pdfGoogle Scholar

9.

Garcia-Gaines, R.A., and Frankenstein, S. 2015. USCS and the USDA classification system: development of a mapping scheme. Final Report. US Army Corps of Engineers. Engineer Research and Development Center, Vicksburg MS. ERDC/CRREL TR-15-4, 46 pp. Google Scholar

10.

Handy, R.L., and Fenton, T.E. 1977. Particle size and mineralogy in soil taxonomy. Transp. Res. Rec. 642: 13–19. Google Scholar

11.

Kingston, M.S., and Presant, E.W. 1989. The soils of the regional municipality of Niagara volumes 1 & 2, Report No. 60 of the Ontario Institute of Pedology, Land Resource Research Centre Contribution No. 89-17. Ministry of Agriculture and Food, and Research Branch, Agriculture Canada. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/on/on60/index.htmlGoogle Scholar

12.

Lamontagne, L., Martin, A., and Nolin, M.C. 2014. Étude pédologique du comté de Napierville (Québec). Laboratoires de pédologie et d'agriculture de précision. Centre de recherche et de développement sur les sols et les grandes cultures. Direction générale des sciences et de la technologie. Agriculture et Agroalimentaire Canada, Québec. [Online]. Available from  https://sis.agr.gc.ca/siscan/publications/surveys/pq/pq42b/pq42b_report.pdfGoogle Scholar

13.

Luttmerding, H.A. 1981. Soils of the Langley-Vancouver map area: Report 15. British Columbia Soil Survey – Volume 6 Technical Data – Soil Profile Descriptions and Analytical Data. Province of British Columbia, Ministry of Environment, Assessment and Planning Division, Kelowna, BC. 345 pp. Google Scholar

14.

Michalyna, W. 1972. Report on soil family. Pages 200–212 inReport on the second meeting of the Western section of the Canada soil survey committee. Kelowna, BC. Feb. 15–17, 1972, 217 pp. Google Scholar

15.

National Soil Survey Committee of Canada (NSSC). 1955. Report on the third conference of the National Soil Survey Committee. Winnipeg, Manitoba. 62 pp. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1955_nssc_3rdmeeting.pdfGoogle Scholar

16.

National Soil Survey Committee of Canada (NSSC). 1963. Report on the fifth meeting of the National Soil Survey Committee of Canada. Winnipeg, Manitoba. 92 pp. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1963_nssc_5thmeeting.pdfGoogle Scholar

17.

National Soil Survey Committee of Canada (NSSC). 1965. Report on the sixth meeting of the National Soil Survey Committee of Canada. Laval University, Quebec. 132 pp. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1965_nssc_6thmeeting.pdfGoogle Scholar

18.

National Soil Survey Committee of Canada (NSSC). 1968. Proceedings of the seventh meeting of the National Soil Survey Committee of Canada. The University of Alberta, Edmonton. Apr. 22–26, 1968, 216 pp. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1968_nssc_7thmeeting.pdf (soilsofcanada.ca). Google Scholar

19.

Pawluk, S. 1970. Report of subcommittee on soil survey interpretations for engineering proposes. Proc. 8th Meeting Nat. Canada Survey Committee of Canada. pp. 77–85. [Online]. Available from  https://soilsofcanada.ca/documents/national_soil_survey_proceedings/1970_cssc_8thmeeting.pdfGoogle Scholar

20.

Presant, E.W., and Wicklund, R.E. 1971. The soils of Waterloo county, Report No. 44 of the Ontario Soil Survey, Research Branch, Canada Department of Agriculture and the Ontario Agricultural College. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/on/on44/index.htmlGoogle Scholar

21.

Schoeneberger, P.J., D.A. Wysocki, E.C. Benham, and Soil Survey Staff. 2012. Field book for describing and sampling soils, Version 3.0. Natural Resources Conservation Service, National Soil Survey Center, Lincoln, NE. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/on/on58/index.htmlGoogle Scholar

22.

Sims, R.A. Towill, W.D., Baldwin, K.A. and Wickware, G.M. 1989. Field guide to the forest ecosystem classification for Northern Ontario, Ontario Ministry of Natural resources. 199 pp. [Online]. Available from  https://cfs.nrcan.gc.ca/publications?id=22144Google Scholar

23.

Soil Classification Working Group (SCWG). 1998. The Canadian system of soil classification. 3rd ed. Agriculture and Agri-Food Canada, Publ. 1646, (revised) NRC Research Press, Ottawa, 187 pp. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/manuals/1998-cssc-ed3/index.htmlGoogle Scholar

24.

Soil Science Division Staff (SSDS). 2017. Soil survey manual. InUSDA handbook 18. C. Ditzler, K. Scheffe, and H.C. Monger. (eds). Government Printing Office, Washington, DC. Chapter 3 Examination and Description of Soil Profiles. [Online]. Available from  https://www.nrcs.usda.gov/wps/portal/nrcs/detailfull/soils/ref/?cid=nrcs142p2_054262Google Scholar

25.

United States Department of Agriculture (USDA). 1987. Soil Mechanics Level I, Module 3, USDA Textural Classification, Study Guide, National Employee Development Staff, Soil Conservation Service, USDA, revised February 1987. Google Scholar

26.

Wang, C., and Rees, H.W. 1983. Soils of the Rogersville-Richibucto region of New Brunswick. New Brunswick Soil Survey Report No. 9. LRRI Contribution No. 89. Land Resource Research Institute, Ottawa, Ontario. Research Branch, Agriculture Canada and New Brunswick Department of Agriculture and Rural Development. [Online]. Available from  https://sis.agr.gc.ca/cansis/publications/surveys/nb/nb9/nb9_report.pdfGoogle Scholar

27.

Warren, C.J., Saurette, D.D., Heck, R.J., and Comeau, L.P. In press. Proposed new soil order – Leptosolic order for Canadian System of Soil Classification.. Can. J. Soil Sci. In press. Google Scholar
© 2022 The Crown.
C. James Warren and Daniel D. Saurette "Proposed changes to the soil family taxon within the Canadian System of Soil Classification," Canadian Journal of Soil Science 102(2), 409-418, (18 January 2022). https://doi.org/10.1139/CJSS-2021-0146
Received: 5 October 2021; Accepted: 7 January 2022; Published: 18 January 2022
KEYWORDS
Canadian System of Soil Classification
famille de sols
granulométrie
Particle size
pédologie
pedology
soil family
Back to Top