Content uploaded by Amin Ismayilov
Author content
All content in this area was uploaded by Amin Ismayilov on Dec 19, 2020
Content may be subject to copyright.
Available via license: CC BY-SA
Content may be subject to copyright.
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
202
The correlation of Azerbaijan arid soils with WRB-2014
Amin İsmayilov, Maharram Babaev, Fikrat Feyziyev*
Institute of Soil Science and Agrochemistry of Azerbaijan National Academy of Science, AZ10073, Baku, Azerbaijan
Abstract
Article Info
Received : 21.11.2019
Accepted : 11.04.2020
The geographical principles are used in grouping of the soils the highest taxonomic standards
in the soviet soil scientists works concerning the classification. But the Azerbaijan soil
classification is based on genetic profile. Traditionally – topographic, color, climate and so on
names are used in this classification, which in the soils genetic types idea is assumed as a
basis. The International classification system is identified on the basis of the diagnostic
parameters in the field researches and specified as a result of the laboratory analyses. The
Azerbaijan soil classification consists of eight taxonomic level and a high taxonomic level is
considered- soil class, section, genetic soil type, low soil taxa - soil gender, sort, diversity, row,
soil variants. Mainly used central taxon is soil type. An aim of the research is to determine
correlative chances of WRB-2015 International soil classification system with the Azerbaijan
soil classification. It was detected that a correlation of both soil classifications is possible. The
correlation is taken place in different taxon levels. Therefore, the soils were analysed at a type
and subtype standard besides high taxas when the soils were correlated. As a result of
correlation, it was defined that irrigated meadow-grey soils should be correlated Anthrosols,
but meadow-grey soils concerned Calcisols and Gleysols.
Keywords: Correlation, WRB, Anthrosols, Calcisols, classification, meadow-grey soils.
© 2020 Federation of Eurasian Soil Science Societies. All rights reserved
Introduction
Soil classification is a means which have traditional and necessary importance in performing of the scientific
and applied works in connection with the correct and expedient management of the soil productivity and
registration of the soil resources. The soil classification is the form of defining soil diversities and also
expanding of researches and modernization of soil reserves (Lebedeva et al., 2005; Sarmast et al., 2016). It is
also an important instrument in the communication of soil research results at and international levels of soil
science (Zádorová and Penížek, 2011; Rozhkov, 2012). Soil classifications are dynamic systems and their
changes are closely related to the latitude of thought of soil researchers and the level of knowledge about
soils. Yet soil classification principles should remain consistent with the geographical features of territory’s
evolution (Lebedeva and Gerasimova, 2009). There is a special soil researche program in every country some
of them are fulfilled at an economical standard, some at state standard and some at national standard. Two
approaches are available in soil classification establishment classification based on genetics and diagnostics
(Bockheim and Gennadiyev, 2000). The first soil classification was established by the Russia soil scientists and
built on genetic principles according to Dokuchaev΄s soil forming theory (Gerasimova, 2015).
Azerbaijan is one of such regions by its large specter of the horizontal and vertical soil zones more diversity of
the lowest taxons and soil types. The modern soil regime processes are a basis of the Azerbaijan soil
classification by paying attention to soil features and soil forming factors. The Azerbaijan soils classification
was prepared by a genetic-profile principle. The classification taxa diagnostics on the basis of the soil profile
structural characters is given by suggesting of the soils' division on genetic profile and this approach gives a
chance to pay attention to all the natural and anthropogenic changed soils in the single soil classification.
Amin İsmayilov
:
amin.ismayil@gmail.com
:
0000-0003-1878-415X
Maharram Babaev
:
babayev.mp@gmail.com
:
0000-0001-8337-1701
*
Fikrat Feyziyev
:
fikrat.fm@gmail.com
:
0000-0001-9771-9799
(Corresponding author)
e-ISSN
:
2147-4249
DOI
:
https://doi.org/10.18393/ejss.724698
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
203
According to Salaev (1991), an ecological-genetic classification is more separated taxa system than other
classification systems type- subtype-gender-sort. According to this approach the Azerbaijan soil map scaled as
1׃100000 was prepared (1998) and adopted for the soil classification at a country’s standard. As above
mentioned, an available classification system of Azerbaijan soils is characterized regionally and its correlation
to the International soil classification is necessary for participation in the integration process under the
modern globalization condition. As it is known, WRB soil classification system (FAO, 2015) is rather good for a
national classification systems correlation, because the international correlation chances were taken into
account while establishing this system, it is used for the middle and little scaled maps classification very much
(Krasilinikov, 2009). There were efforts by several researchers in a correlation direction of the national soil
classification based on genetic profile for the WRB. One of the main problems is the utilization of the different
analysis methods for definition of the soil diagnostic indications and information shortage causes definite
mistakes during correlation (Reintam and Koster, 2006; Urushadze et al., 2016). Though the Azerbaijan Soil
Resources were investigated before the XX century, since 1945 they were begun to be studied in institutional
form. Factually majority of the methods used in soil analyses is ancient and isn’t used for WRB classification
by International Union of Soil Sciences (IUSS). Though there is enough information about Azerbaijan soil
resources for the local use, but its utilization in an international scale is difficult. It makes definite difficulty in
integration to the International Soil Science. The differences and connections between the World Reference
Base for Soil Resources and the Azerbaijan soil classification system were first summarized by Krasilnikov et
al. (2009) who also established correlation keys primarily based on field experiences and the definitions of the
classification units. However, they pointed out that the classes of the two systems cannot match due to their
different approach and methodology. At present, the development of international cooperation in different
sciences, including soil science, poses the problem of the creation of a new soil classification system that
should be based not only on the regional and national classification concepts but also linked with the
internationally accepted soil classification systems (Babaev et al., 2006; Gerasimova, 2015). An increasing
demand for harmonized digital soil information can be observed nowadays. The correlation of national
systems with WRB has got a new priority, as it is necessary for the development of European and global
databases, giving the opportunity to enrich them with more new data (Kabała et al., 2015). The former Soviet
countries mainly used form the classification grounded on genetic profile (Shishov, 2004), last years the
correlation process is performing for the WRB international classification system. In this direction the expert
based, concept based and centroid based methods are mostly used, these methods effectively help the
correlation process (Lang, 2013). The research aim is to investigate a correlation of the Azerbaijan soil
classification to the WRB soil classification and to define their different and unlike characters. As a research
object the meadow grey, irrigated meadow-grey soils which are dominant soil type for the Azerbaijan zone
have been taken.
Material and Methods
The study area was Mugan plain, located the central part of Kur-Araks lowland between 39˚43'18″ N and
39˚44'40″N latitude and 47˚58'14″ and 48˚57'32 E longitude covering an area of 4500 km2. It has an arid
climatic condition and a quantity of the rainfalls is 180-250 mm. Evaporation is between 800-1000 mm.
Annual average temperature changed between 14-15 º C. The arid sone of Azerbaijan characterized with its
agrarian importance and soils mainly used under different agricultural plants such as wheat, barley, cotton,
lucerne and vegetables. The main part of research area is located under sea level for this reason soils
genetically have high risk to salinization. The elevation of the main part of the research area is located under
sea level and changed between -37-50 m. Most of the current topography is a result of post-glacial processes
during the quaternary period. The low elevation areas are mainly covered by alluvial, marine and lacustrine
materials.
The WRB-2014 (2015 update) criteria which were adopted by the world soil scientists were assumed as a
basis. While investigating the correlation opportunities the method (Minasny et al., 2010) based on
conception and Krasilnikov et al. (2009) approaches were used. The last version of the Azerbaijan soil
classification was in 2011 (Babaev et al., 2011) and the main taxa were determined.
45 soil pedons were excavated in the research area. The main soil types are meadow-grey and irrigated
meadow-grey soils. On field checks, the geographical positions of representative soils for each site were
determined by Global Positioning System. The soil profiles were excavated and described according to the
“Guidelines for soil description” (FAO, 2006). Soil samples from different genetic horizons were taken, and
samples were air dried, crushed, and passed through a 2 mm sieve. Pipette method was used for texture
analysis (Gee and Bauder, 1986), Organic matter by Walkley–Black method (Walkley and Black, 1934),
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
204
calcium carbonate by calcimetric method (Loeppert and Suarez, 1996), cation exchange capacity by was
defined as sum of exchangeable cations (Bower and Hatcher, 1966), pH and EC by pH-meter and EC-meter.
Figure 1. Study area (soil pedon distribution and natural color composition)
A last version of the Azerbaijan soil classification was printed in 2011 (Babaev et al., 2011). The Azerbaijan
soil classification consists of 3 classes, 15 sections, 37 types, 90 subtypes, 146 genders, (species); 388 sorts,
140 diversities, 157 rows, 47 variants. This variety forms large information about the soils and simplifies
correlation opportunities. The soil passports (over the types) prepared according to the Azerbaijan soil
classification rules and Azerbaijan Soil Map with the scale of 1׃100000 were used. Soils were classified
according to the WRB (FAO, 2015) soil classification systems. Finally, the soil units of WRB were compared
with Azerbaijan soil classification based on genetic properties.
Results and Discussion
The irrigated meadow-grey, meadow-grey soil types which are dominant for the Azerbaijan arid soil zone
were taken in order to investigate the correlation opportunities to the WRB soil classification. Azerbaijan
soil classification were correlated the at a type level and determined the principal soil types paying attention
to the main soil forming character concerning the WRB 2006 version (Babaev, 2018). This process has not
realized in the low taxa. However, one soil type concerns 2 Soil Reference Group (RSG) in the WRB in some
cases. On the other hand, the small taxa which are taken as a diagnostic indication in the Azerbaijan soil
classification aren’t characteristic for the WRB RSG in some cases. Therefore, using of more information is
rather important while performing the WRB correlation process. The Azerbaijan soil classification is
hierarchic structural. The greatest taxon is considered soil class, the smallest taxon is considered a variant.
In general the Azerbaijan classification involves two units system. A high taxonomic level-soil class, section,
genetic soil type. The low soil taxons-soil gender, sort, diversity, row, soil variants paying attention to the
soil fruitfulness ability. Prior to elaboration of the new Azerbaijan soil classification system a complete
systematized list of soils was compiled on the basis of the explication to the soil map of Azerbaijan on a scale
of 1׃100000, which characterizes in detail the spatial distribution of different genetic soil groups (Babayev et
al., 2006). Correlation of the meadow-grey and irrigated meadow-grey soils to the WRB was identified as
Calcisols in the first initiative performed according to the archive materials. A main diagnostic indication in
definition of these soils as an independent soil type is a sign of the oxidation-reduction process which is
formed by subsoil water in the location depth and soil profile. Meadow-grey soil type developed under the
winter pastures in the plain zones. The soil profile thickness is >120 cm. There are two subtypes. The ground
waters in the meadow-grey subtype are situated below 200 cm and oxidation- reduction processes mainly
occur B and C horizons (Babayev, 1984).
Gleying is observed beginning of B layer in the profile as a result of the ground waterseasonal fluctuation in
the meadow-grey soils. The soil profile is calcareous and an average quantity of carbonates is 10,8%. As a
result of the high evaporation CaCO3 or gypsum accumulation on the upper layers is characterized by the
ground waters. The quantity of carbonates on the topsoil changed between 3.8-141.7 g/kg and mean values
is 103.3 g/kg. But within the profile the value of carbonates increased (46.7- 215.8 g/kg). A quantity of
organic substances changes by 1,5-3%, pH -8-9. On the other hand, salinized–solonetzificated process is
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
205
characteristic for the soil profile and the dissolved salts are accumulated at 50 cm of depth. These soils
correlate to Haplic Calcisols (Gleyic, Salic). These soils spread in an associated form with the saline soils. A
main characteristic feature of the Calcisols is accumulation of secondary carbonates in the soil profile.
Oxidation-reduction process indications which are created under the groundwater effect are taken into
account at a second level. Though this process was clearly given in the national classification, it was
distinguished in the gender and sort taxa. The main morphological characteristics of characteristic pedons
were given in Table 1. A main characteristic feature in the irrigated meadow–grey soil type is Irragric
horizon formation as a result of the long irrigation and cultivation. The irrigated meadow-gray soils of the
study area have been formed on the Araks river basin. These soils are irrigated by the channels separated
from Araks River. Araks river has high content of mineral and nutritional content. The mineralization of
irrigation water is 560-880 mg/l. Morphological and diagnostic indicators of soil have changed considerably
as a result of irrigation of cultivated areas using these waters.
Figure 2. Gleysols (a), Calcisols (c) and Anthrosols (c) of Mugan lowland
The main reason of formation of pedodiversity on the type level is the changing of soil formation processes.
In this case, it forms the changes in soil taxa and the current taxon’s isn’t enough to describe soil
classification systems in global way (Bockheim and Gennadiyev, 2000).
In any case, guarding of the natural structure is impossible, because majority of the soil is under
anthropogenic impact to some or other degree. Babaev (1984) consolidated such soils in the highest taxa
anthropogenic changed soils class paying attention to the long anthropogenic, especially irrigation impact.
The agroirrigation horizon was formed in the soil profile by the impact of the long irrigation and cultivation
in morphogenetic diagnostics of these soils. Thickness of this layer is more than 50 cm. The soil profile
became dark, humus was washed into the deep layers. The burial state exists in these soils (Figure 2).
Correlation of this soil type to the WRB confirms with the Anthrosols RSG and the Irragric Anthrosols
(Gleyic, Loamic) soils were formed. As is seen the correlation to the WRB occurs in the highest taxon-class
level in this soil type.
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
206
Table 1. Morphological characteristics of studied pedons
Profile
No and
cordinates
Horizon
Depth
Boundary
Colour
Consistency
(moist)
Structure
Effervescence
Texture
Moist
Dry
S13
39º33'02 N
48º36'36 E
Ap
0-16
GS
10YR4/3
10YR7/1
LO
GR
MO
Silty-clay
A1
16-30
GS
10YR4/2
10YR7/4
FR
AB
ST
Silty-clay
ABc
30-58
GS
10YR5/4
10YR7/4
VFR
MA
MO
Silty-clay
Bk
58-92
CS
10YR4/4
10YR7/3
VFR
MA
ST
Clay
CBz
92-124
CS
10YR5/3
10YR7/2
VFR
BL
ST
Clay
S16
39º26'28 N
48º31'16 E
Ap
0-18
GW
10YR5/3
10YR6/4
FR
SG
ST
Silty-clay
A1
18-33
GS
10YR5/3
10YR6/2
FR
SA
ST
Silty-clay
AB
33-57
CS
10YR4/2
10YR7/3
FR
SA
ST
Silty-clay
Bg
57-94
AS
10YR5/3
10YR6/3
FR
AS
ST
Silty-clay
Cr
94-132
AS
10YR5/3
10YR7/2
FR
AS
ST
Silty-clay
S19
39º40'30
48º38'41 E
A
0-8
CS
10YR3/2
10YR5/2
VFR
MA
ST
Clay-loam
A1
8-26
CS
10YR3/2
10YR6/2
VFR
SN
ST
Silty-clay-loam
Bc
26-49
CS
10YR6/4
10YR7/1
FR
SA
ST
Silty-loam
BCc
49-78
CS
10YR5/4
10YR8/1
FR
AS
ST
Silty-loam
Cg
78-109
CS
10YR5/3
10YR8/2
FR
AS
ST
Silty-loam
S20
39º43'35 N
48º33'37 E
A
0-9
CS
10YR3/2
10YR6/3
FR
AB
ST
Silty-loam
AB
9-30
CS
10YR6/4
10YR8/3
FR
SB
ST
Silty-loam
Bg
30-58
CS
10YR6/5
10YR7/4
MFR
M
ST
Silty-clay-loam
BCg
58-89
CS
10YR5/5
10YR7/3
SH
M
ST
Silty-clay
Cg
89-118
CS
10YR4/3
10YR6/3
SH
M
ST
Silty
S31
39º36'34 N
48º57'11 E
Ap
0-23
GW
10YR6/2
10YR8/2
VFR
SG
ST
Silty-clay-loam
A1
23-49
GS
10YR5/4
10YR7/2
FR
SB
ST
Silty-clay-loam
Bk
49-81
CS
10YR5/2
10YR7/3
FR
SB
ST
Silty-clay-loam
BCk
81-114
CS
10YR7/4
10YR8/2
MFR
SB
ST
Silty-clay-loam
S35
39º56'60 N
48º49'22 E
Ap
0-20
GW
10YR4/3
10YR6/3
FR
GR
ST
Silty-clay-loam
A1
20-30
GS
10YR4/2
10YR6/2
FR
AS
ST
Loam
AB
30-74
GS
10YR5/3
10YR7/3
VFR
AS
ST
Silty-clay-loam
Bg
74-88
CS
10YR4/1
10YR7/1
VFR
SA
ST
Silty-clay-loam
Cg
88-126
CS
10YR6/3
10YR8/4
VFR
SB
ST
Silty-clay-loam
S41
39º49'20 N
48º25'30 E
Ap
0-26
GS
10YR4/3
10YR8/3
FI
GR
ST
Silty-clay-loam
A1
26-48
GS
10YR4/4
10YR7/3
FR
AB
ST
Silty-clay-loam
ABk
48-76
CS
10YR5/4
10YR7/3
FR
SA
ST
Silt-loam
Bg
76-99
CS
10YR4/3
10YR7/4
FR
MA
ST
Silty-clay-loam
BCg
99-138
CS
10YR4/4
10YR8/4
FR
MA
ST
Silt-loam
Boundary: distinctness (A-abrupt, C-clear, G-gradual); topography (S - smooth, W - wavy). Consistency: moist (L- loose, VFR - very
friable, FR- friable, FI- firm, VFI-very firm). Structure: type (AS-angular and subangular block, AB - angular blocky, SB - subangular
blocky, SG-single grain, SA- subangular and angular blocy MA - massive). Effervescence: class (ST - strongly effervescent, MO-
moderately).
Conclusion
The Azerbaijan soil classification is called according to morphology, colour, climate, topographic and so on
and the chemical parameters are characterized diagnostically. Some of the small taxa aren’t used in
correlation. For example, the differentiation isn’t performed in WRB for the soil profile density and cultured
level which include in the small taxon-row and variant. The results showed that the correlation of the low
taxa gender, sort and diversity used in the national soil classification to the WRB is possible. The Azerbaijan
soil classification correlation based on genetic profile can be occurred at different levels. Sometimes
correlation to the WRB does not result positively at a type level and it can conform to the separate Soil
Reference Group at the subtypes level that includes in the type. The soil formation direction is assumed a
basis while the soil types are divided into subtypes in the Azerbaijan soil classification in any case.
Therefore, the correlation is also observed at a subtype level. The smallest taxa conform to the main and
additional qualifications. It is possible to correlate the Azerbaijan soil classification based on genetic profile
to the WRB at a different taxon level paying attention to an analogy of the soil forming process. But there is a
great need for high perceptibility and expert discussion in this problem. While establishing the Azerbaijan
soil classification a great scaled map is assumed as a base map and it is mainly local applied characteristic.
A. İsmayilov et al. / Eurasian J Soil Sci 2020, 9 (3) 202 - 207
207
References
Babaev, M.P., 1984. Irrigated soils of the Kura-Araks lowland and their productive capacity. Elm. Baku, Azerbaijan.
176p. [in Russian].
Babaev, M.P., Dzhafarova, Ch.M., Gasanov, V.G., 2006. Modern Azerbaijani soil classification system. Eurasian Soil Science
39(11): 1176-1182.
Babaev, M.P., İsmayilov, A.İ, Huseynova, S.M., 2017. The correlation of Azerbaijan national soil classification with WRB.
Elm. Baku, Azerbaijan. 271p.
Babaev, M.P., Jafarova, Ch.M., Hasanov, V., 2006. Modern classification of Azerbaijan soils. Elm. Baku, Azerbaijan. 360p.
Bockheim, J.G., Gennadiyev, A.N., 2000. The role of soil-forming processes in the definition of taxa in Soil Taxonomy and
the World Soil Reference Base. Geoderma 95(1-2): 53-72.
Bower, C.A., Hatcher, J.T., 1966. Simultaneous determination of surface area and cation exchange capacity. Soil Science
Society America Journal 30(4): 525–527.
FAO, 2006. Guidelines for soil description. Fourth edition. FAO. Food and Agriculture Organization of the United
Nations, Rome, Italy. 97p. Available at [Access date: 21.11.2019]: http://www.fao.org/3/a-a0541e.pdf
FAO, 2015. World reference base for soil resources 2014. International soil classification system for naming soils and
creating legends for soil maps. Update 2015. World Soil Resources Reports No. 106. Food and Agriculture
Organization of the United Nations, Rome, Italy. 192p. Available at [Access date: 21.11.2019]:
http://www.fao.org/3/i3794en/I3794en.pdf
Gee, G.W., Bauder, J.W., 1986. Particle-size Analysis. In: Methods of Soil Analysis, Part 2, Chemical and Microbiological
Properties, A.L. Page, R.H. Miller, D.R. Keeney (Eds.), 2nd Edition. Agronomy Monograph No. 9, American Society
of Agronomy, Soil Science Society of America. Madison, Wisconsin, USA. pp. 383-411.
Gerasimova, М.I., 2015. Principles, structure and taxonomic units in the Russian and International (WRB) systems of
soil classification. Bulletin of the V.V. Dokuchaev Soil Science Institute 79: 15-25.
Kabała, C., Świtoniak, M., Charzyński, P., 2016. Correlation between the Polish Soil Classification (2011) and
international soil classification system World Reference Base for Soil Resources (2015). Soil Science Annual
67(2): 88-100.
Krasilnikov, P., Marti, J.J.I., Arnold, R., Shoba, S., 2009. A handbook of soil terminology, correlation and classification.
Taylor & Francis Ltd, London, UK. 448p.
Láng, V., Fuchs, M., Waltner, I., Michéli, E. 2013. Soil taxonomic distance, a tool for correlation: As exemplified by the
Hungarian Brown Forest Soils and related WRB Reference Soil Groups. Geoderma 192: 269-276.
Lebedeva, I.I., Gerasimova, M.I., 2009. M.I. Factors of soil formation in soil classification systems. Eurasian Soil Science
42: 1412-1415.
Lebedeva, I.I., Tonkonogov, V.D., Gerasimova, M.I., 2005. Anthropogenic pedogenesis and the new classification system
of Russian soils. Eurasian Soil Science 38(10): 1026-1031.
Loeppert, R.H., Suarez, D.L., 1996. Carbonate and gypsum. In: Methods of Soil Analysis, Part 3 - Chemical Methods.
Sparks, D.L., Page, A.L., Helmke, P.A., Loeppert, R.H., Soltanpour, P.N., Tabatabai, M.A., Johnston, C.T., Sumner, M.E.
(Eds.). American Society of Agronomy Inc., Madison, Wisconsin, USA. pp. 437-475.
Minasny, B., McBratney, A.B., Hartemink, A.E., 2010. Global pedodiversity, taxonomic distance, and the World Reference
Base. Geoderma 155(3-4): 132-139.
Reintam, E., Köster, T., 2006. The role of chemical indicators to correlate some Estonian soils with WRB and Soil
Taxonomy criteria. Geoderma 136(1-2): 199-209.
Rozhkov, V.A., 2012. Classiology and soil classification. Eurasian Soil Science 45: 221–230.
Salaev, M.E., 1991. Diagnosis and classification of soils of Azerbaijan. Elm. Baku, Azerbaijan [in Russian].
Sarmast, M., Farpoor, M.H., Boroujeni, I.E., 2016. Comparing Soil Taxonomy (2014) and updated WRB (2015) for
describing calcareous and gypsiferous soils, Central Iran. Catena 145: 83-91.
Shishov, L.L., Tonkonogov, V.D., Lebedeva, I.I., Gerasimova, M.I., 2004. Classification and diagnostics of soils of Russia.
Oykumena, Smolensk. 342p. [in Russian].
Urushadze, T., Blum, W., Kvrivishvili, T., 2016. Classification of soils on sediments, sedimentary and andesitic rocks in
Georgia by the WRB system. Annals of Agrarian Science 14(4): 351-355.
Walkley, A.J., Black, I.A., 1934. Estimation of soil organic carbon by the chromic acid titration method. Soil Science 37(1):
29-38.
Zádorová, T., Penížek, V., 2011. Problems in correlation of Czech national soil classification and World Reference Base
2006. Geoderma 167-168: 54-60.