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Digital soil map of Cyprus (1:25,000) AGWATER Options for sustainable agricultural production and water use in Cyprus under global change Scientific Report 6 Deliverable D15, D16 Zomenia Zomeni 1 , Corrado Camera 2 , Adriana Bruggeman 2 , Andreas Zissimos 1 , Irene Christoforou 1 , Jay Noller 3 1 Geological Survey Department of Cyprus 2 Energy, Environment and Water Research Center, The Cyprus Institute 3 Department of Crop and Soil Science, Oregon State University Nicosia, 15 November 2014

Digital soil map of Cyprus (1:25,000)

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Page 1: Digital soil map of Cyprus (1:25,000)

Digital soil map of Cyprus (1:25,000)

AGWATER

Options for sustainable agricultural production and water use in Cyprus under global change

Scientific Report 6

Deliverable D15, D16

Zomenia Zomeni1, Corrado Camera2, Adriana Bruggeman2,

Andreas Zissimos1, Irene Christoforou1, Jay Noller3

1 Geological Survey Department of Cyprus

2 Energy, Environment and Water Research Center, The Cyprus Institute

3 Department of Crop and Soil Science, Oregon State University

Nicosia, 15 November 2014

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Table of Contents

ABSTRACT ...................................................................................................................................................................... 2

INTRODUCTION ............................................................................................................................................................ 3

METHODS ........................................................................................................................................................................ 3

DATA ................................................................................................................................................................................. 4

TRAINING DATA ............................................................................................................................................................. 4

PREDICTORS ................................................................................................................................................................... 5

DERIVED SOIL SERIES MAPS ........................................................................................................................................... 7

DERIVED SOIL PROPERTIES MAPS ................................................................................................................................... 7

RESULTS .......................................................................................................................................................................... 9

SOIL SERIES MAP ............................................................................................................................................................ 9

SOIL PROPERTY MAPS ................................................................................................................................................... 11

REFERENCES ............................................................................................................................................................... 14

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ABSTRACT

Considering the increasing threats soil are experiencing especially in semi-arid,

Mediterranean environments like Cyprus (erosion, contamination, sealing and salinisation),

producing a high resolution, reliable soil map is essential for further soil conservation studies.

This study aims to create a 1:25.000 soil map covering the area under the direct control of the

Republic of Cyprus (5.760 km2).

The study consists of two major steps. The first is the creation of a raster database of

predictive variables selected according to the scorpan formula. It is of particular interest the

possibility of using, as soil properties, data coming from three older island-wide soil maps

and the recently published geochemical atlas of Cyprus. Electric conductivity, pH, total

carbon and the Mafic Index of Alteration (MIA-R) were selected to represent soil properties;

maximum and minimum temperature for climate; organic carbon for organic matter; the

DEM and related relief derivatives (slope, aspect, curvature, landscape units); and bedrock

and surficial geology for parent material and age.

In the second step, the digital soil map including soil series and soil properties (depth and

texture) is created using the Random Forests package in R. Random Forests is a decision tree

classification technique where many trees, instead of a single one, are developed and

compared to increase the stability and the reliability of the prediction. The model is trained

and verified on areas where a 1:25.000 published soil maps obtained from field work is

available and then it is applied for predictive mapping to the other areas.

Results shown that the average error of the model, both for soil series and soil properties, is

around 10%, demonstrating the robustness of the methods proposed.

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INTRODUCTION

The soils of Cyprus are unique due to the geological complexity, the Mediterranean island

climate and the long presence of man on the landscape. The geology of Cyprus is dominated

by the Troodos Ophiolite, which is a fragment of a fully developed oceanic crust, consisting

of plutonic, intrusive and volcanic rocks and chemical sediments. Sedimentary formations

cover the coastal plains in the south and the intermountain plain in the north. The soils on

Cyprus vary between lithosols, leptosols, regosols, gypsisols, solonchaks, solonetz, vertisols,

and cambisols based on the WRB (World Reference Base) of FAO (Food and Agriculture

Organization of the United Nations) soil classification system (FAO, 1989). They are

generally poor in organic matter (Koudounas, and Makin, 1981; Grivas, 1988) and closely

associated to parent material and landscape position. An incomplete series of soil surveys and

maps at a scale of 1:25,000 have been prepared by the Soil Section of the Department of

Agricultural from 1967-1985, using traditional field survey methods The soils are mapped

and classified based on their development stage, origin and parent material. These maps

formed the basis of the development of a digital soil map of Cyprus at a scale of 1:250,000.

The aim of the study was to create, using digital soil mapping techniques, a soil map of

Cyprus (including soil series and soil properties) at 1:25,000 scale. This involved the creation

of digital soil data to be used as training data and the creation of other data of physical

parameters involved in the soil forming process to be used as predictors. The analysis was run

for areas under the effective control of the government of the Republic of Cyprus were data

were available.

METHODS

The soil series and soil property maps are calculated using Random Forest. Random Forest is

a multiple tree classification and regression method developed by Leo Breiman (2001). A

clear overview of the method’s functioning is presented by Boulesteix et al. (2012) and

summarized in Figure 1. Each tree is a standard classification tree. At each node the code

randomly samples N (mtry) predictors and it picks the predictor that ensures the best split,

evaluated by the decrease of Gini impurity (DGI). A bootstrap sample from the original data

set is used to build a tree. Each target point is then classified aggregating the trees and

picking the class that received the major number of votes. A very relevant feature of Random

Forest is the out-of-bag (OOB) error. As stated, trees are calculated using a bootstrap sample

from the original data set, this means that some values are not actually used to construct the

trees. Therefore these data can be used for validation purpose. The OOB error is the average

error, calculated for each target class, coming from the comparison of the observations that

have been left out and the model output. An additional feature of Random Forest is the

capacity to rank the relative importance of the variables in the prediction.

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Figure 1: flow chart explaining the functioning of the Random Forest algorithm (from Boulesteix et al.,

2012)

DATA

Training Data

The sample data for deriving the train and out-of-bag data were based on published soil maps.

These detailed soil maps have a 1:25,000 scale with only ten out of the forty-some possible

sheets having been published to date (Figure 2). By far the most detailed soil reference on the

island are these ten 1:25.000 scale soil sheets (Soteriades and Georgiades, 1967, Soteriades

and Grivas, 1968, Soteriades, Koudounas and Markides 1968, Soteriades.and Markides,

1969, Grivas and Georgiades, 1972, Markides, 1975, Koumis, 1980a, Koumis, 1980b,

Koumis, 1980c, Markides, 1985) which are always accompanied by a land suitability for

agriculture map. Two of them, the Pafos sheet (Soteriades and Koudounas, 1968) and the

Polemi sheet (Markides, 1973) are also accompanied by extensive soil memoirs. These ten

soil sheets form the basis for the most detailed and thorough digital soil information on the

island.

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Figure 2: Soil map of Cyprus and availability of soil maps at the 1:25,000 scale (from the Soil Map of

Cyprus (1999), by the Soil and Water Use Section, Cyprus Department of Agriculture).

The maps were scanned, georeferenced and digitized in a GIS environment. The resulting

dataset is a merge of the 10 soil maps and consists of with 11.000 polygons classified in 52

soil series with further 4-8 subseries classification for each series. The dataset was converted

to raster format with cell size of 25 x 25 m2 and used as training data for the training areas in

building the multiple tree classification.

Predictors

Predictors have been selected according to the scorpan formula (McBratney et al., 2003) and

include physical variables like relief, climate, geology, geomorphology, and geochemistry

(Table 1). Some graphical examples of these data are shown in Figure 3.

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Table 1: predictors used in the model.

Short

name Description

Source Source

scale

pH pH measured from a surface soil sample and ranging between 0-9 Cohen et al., 2011 1 km grid

EC Electrical conductivity measured from a surface soil sample and ranging between

0-20 ms/cm Cohen et al., 2011 1 km grid

TotC Total Carbon measured from a surface soil sample and expressed in % Cohen et al., 2011 1 km grid

OrgC Organic Carbon measured from a surface soil sample and expressed in % Cohen et al., 2011 1 km grid

Miar Mafic Index of Alteration derived from various geochemical parameters Cohen et al., 2011 1 km grid

DEM Digital Elevation Model with a 25m grid created from 24 digitized topographical

maps of Cyprus (contours and trigonometrical points) Series K717 1:50.000

Aspect Aspect, derived from Digital Elevation Model using ArcGIS 3-D Analyst Derivative of DEM 1:50.000

Curv Curvature, derived from Digital Elevation Model using ArcGIS 3-D Analyst Derivative of DEM 1:50.000

Slope Slope [deg] derived from Digital Elevation Model using ArcGIS 3-D Analyst Derivative of DEM 1:50.000

Quat Quaternary Geology (surficial geology), with 5.900 polygons in many categories

according to depositional environment and relative age Noller, 2009 1:50.000

Bedrock

Geological Map of Cyprus based on the digitisation and merge of numerous

published and unpublished geological maps of the Cyprus Geological Survey,

contains 14.000 polygons in hundreds of classes pertaining to age and formation

Digital data of Cyprus

Geological Survey 1:50.000

LU Landuse (CORINE, 2006) Büttner and Kosztra, 2007 1:250.000

GLU Geomorphological Landscape Units, with 29.300 polygons in 9 categories

according to landscape position, derived from Digital Elevation Model Noller, 2009 1:50.000

Tmax Mean maximum temperature (July) Camera et al., 2013 1 km grid

Tmin Mean minimum temperature (January) Camera et al., 2013 1 km grid

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Figure 3: Input rasters of some selected variables are shown here in western Lemesos district at a scale of

1:300,000. Quaternary geology (top left), slope (top right), Landscape units (bottom left) and pH (bottom right).

Derived Soil Series maps

In detail, 52 soil series were recognized across the island and all of them are present in the training

areas. To train the model, a random selection from 50% of the area covered by the existing 1:25,000

soil maps (approximately one million points) and a total of 350 trees have been created. The

number of selected training points and trees is the maximum that the available computing facilities

allowed. The model has been run at the High Performance Computing (HPC) facility of the Cyprus

Institute (Cy-Tera) in Lefkosia.

Derived Soil Properties maps

From the existing ten 1:25,000 sheets (Soteriades and Georgiades, 1967, Soteriades and Grivas,

1968, Soteriades, Koudounas and Markides 1968, Soteriades.and Markides, 1969, Grivas and

Georgiades, 1972, Markides, 1975, Koumis, 1980a, Koumis, 1980b, Koumis, 1980c, Markides,

1985) 8 soil depth classes have been identified from the legend descriptions of all the 52 soil series

and many subseries on the maps. Each class is characterized by a depth interval. To end up with a

single value of soil depth for use in the modeling applications, the average of the interval has been

calculated (Table 2).

In the same fashion, 17 soil texture classes have been recognized. However, among the 17 classes

different nomenclature and classification systems were used. Therefore, data was harmonized and

reclassified in 9 consistent classes (Table 3). Available water capacities (AWC) were assigned for

all standard textures according to Saxton and Rawls (2006), except for clay, which was taken from

Allen et al. (1998).

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Soil property maps over the whole study area were created running RandomForest with exactly the

same configuration used for soil series, with the only exception that the previously created soil

series map was used during this run as a predictor.

Table 2: soil depth classes.

Depth class

(from 1:25.000 scale soil maps)

Depth [cm]

(from 1:25.000 scale soil maps)

Depth [cm]

(single value)

Zero 0-10 5

very shallow 10-25 17

very shallow to

shallow 10-50 30

Shallow 25-50 37

shallow to moderate 25-75 50

moderately deep 50-75 57

Deep 75-100 cm 87

very deep > 100 cm 120

Table 3: texture classes and corresponding available water capacities (AWC).

Texture 17 classes Texture 9 classes AWC [%]

rock bedrock 1

gravel gravel 2

sandy loam gravelly gravelly sand 3

coarse

light sand 5

sand

light to medium loamy sand 7

coarse to medium

sandy loam sandy loam 10

medium loam 14

clay loam

medium to fine clay loam 14

moderately heavy

clayee

clay 16 fine

heavy

medium heavy

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RESULTS

Soil Series map

The calculated 1:25,000 soil series map of Cyprus is presented in Figure 4. The mean OOB error in

classifying the 52 soil series over the training area is 0.1, meaning that 10% of the soils are wrongly

classified. In detail, only four soil series show errors higher than 0.2 (Figure 5), demonstrating the

value of the applied method. The four soil series that are worst classified are: Troodos (class error

0.28), Quarries (error 0.23), Argaki (error 0.22), and Rivers (error 0.20). However, while the errors

are low for the training areas, this does not mean that all the soils of the mapped areas outside the

training areas are correctly predicted. The methodology implicitly assumes that the 10 soil maps

(training areas) are representative for the full mapped area. An obvious problem is the lack of soil

maps for the Troodos massif. Thus, the soils for the Troodos may be not perfectly predicted.

The importance of the different predictors is shown in Figure 6. It is interesting to notice how the

first three predictors, in terms of relative importance, are all geochemistry variables (pH, OrgC,

EC). Therefore, these variables are crucial in the classification process. In Figure 7 the correlations

between the geochemistry variables are shown. These figures demonstrate that the four predictors

are independent of each other.

Figure 4: 1:25,000 soil map of Cyprus obtain with digital soil mapping techniques.

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Figure 5: errors in predicting the 52 soil series

with increasing number of trees in the forest.

The three worst predicted and noisy soils are:.

Figure 6: relative importance of the environmental co-variables used in the classification.

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Figure 7: scatter plots showing how geochemistry variables are correlated to each other.

Soil Property maps

The predicted soil depth and soil texture maps are presented in Figure 8 and Figure 9, respectively.

Similar to the soil series map, the results are very good with the mean error equal to 0.10 (range

0.05 – 0.14) and 0.11 (range 0.05-0.25) for soil depth and texture, respectively. For both maps the

previously predicted, the soil series data, pH and Aspect are the three predictors with the highest

importance in the classification process. It is also worth pointing out that the results in the Troodos

area could not be as good as in the training areas, for the reasons explained in the previous section

(Soil map Series).

In Table 4 a summary of the areal percentages for each class of soil depth and texture is presented.

This gives a quick overview of the amount of land suitable for agriculture (soil depth > 30 cm and

no stoniness).

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Figure 8: 1:25,000 soil depth map of Cyprus obtained through digital soil mapping techniques.

Figure 9: 1:25,000 soil texture map of Cyprus obtained through digital soil mapping techniques.

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Table 4: summary of percentage of the whole study attributed to each soil depth and texture class.

Depth class Depth [cm]

Cell count

%area Texture Cell

count %area

zero 10 509559

5 53.3 bedrock

502694

8 52.5

very shallow 17 521457 5.5 gravel 222 0.0

very shallow to

shallow 30 5865 0.1 gravelly sand 5534 0.1

shallow 37 191014

7 20.0 sand 194037 2.0

shallow to moderate 50 57321 0.6 loamy sand 10090 0.1

moderately deep 57 560850 5.9 sandy loam 93555 1.0

deep 87 137920 1.4 loam 273210

1 28.6

very deep 120 127699

0 13.3 clay loam 160916 1.7

clay 134274

2 14.0

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REFERENCES

Allen, R.G., Pereira, L.S., Raes, D., and Smith, M.: Crop Evapotranpiration: Guildlines for

computing crop water requirements, FAO Irrigation and Drainage Paper No 56. Food and

Agriculture Organisation, Land and Water. Rome, Italy, 1998

Boulesteix, A.L., Janitza, S., Kruppa, J., and König, I.R.: Overview of random forest methodology

and practical guidance with emphasis on computational biology and bioinformatics. WIREs Data

Mining Knowl. Discov. 2, 493–507, 2012

Breiman, L.: Random forests. Mach. Learn. 45, 5–32, 2001

Büttner, G., Kosztra, B.: CLC2006 Technical guidelines. Technical Report No. 17/2007. EEA,

2007. Available from http://www.eea.europa.eu/publications/technical_report_2007_17

Camera, C., Bruggeman, A., Hadjinicolaou, P., Pashiardis, S., and Lange, M.A.: High resolution

gridded datasets for meteorological variables: Cyprus, 1980-2010 and 2020-2050, AGWATER

Scientific Report 5, 70 pp., 2013

Cohen, D.R., Rutherford, N.F., Morisseau, E., and Zissimos, A.M.: Geochemical Atlas of Cyprus.

Sydney: UNSW Press, 2011.

Department of Agriculture, 1999, Section of Soil and Water use, Soil Map of Cyprus, scale

1:250,000

FAO-UNESCO, 1989, Carte mondiale de sols, Legende revisee, Rapport sur les resources en sols

du monde, No. 60, FAO, Rome

Grivas, G.C., and Georgiades, M., 1972, 1:25.000 Sheet 30 Lakatamia, Soil Section, Department of

Agriculture, Ministry of Agriculture and Natural Resources, Cyprus

Grivas, G., 1988, Development of land resources in Cyprus, in Proceedings - Workshop on

conservation and development of natural resources in Cyprus - case studies - soils - groundwater -

mineral resources, Zomenis, S.L., Luken, H., Grivas, G., (editors), published by: Ministry of

Agriculture, Cyprus & Federal Institute for Geosciences and Natural Resources, W. Germany, pp.

7-16

Koudounas, C.; Makin, J., 1981, A study of representative soil profiles from the Limassol - Paphos

districts, Ministry of Agriculture and Natural Resources, Nicosia, 61 p.

Koumis, C.I., 1980a, 1:25.000 Sheet 53 Ypsonas, Soil Section, Department of Agriculture, Ministry

of Agriculture and Natural Resources, Cyprus

Koumis, C.I., 1980b, 1:25.000 Sheet 54 Limassol, Soil Section, Department of Agriculture,

Ministry of Agriculture and Natural Resources, Cyprus

Koumis, C.I., 1980c, 1:25.000 Sheet 58&59 Akrotiri, Soil Section, Department of Agriculture,

Ministry of Agriculture and Natural Resources, Cyprus

Markides, L., 1973, Soils Memoirs of Polemi, Sheet no. 44 & 45, includes 1:25000 map, published

by Ministry of Agriculture and Natural Resources, Department of Agriculture, 138 p

Markides, L., 1975, 1:25.000 Sheet 41 Ormidhia, Soil Section, Department of Agriculture, Ministry

of Agriculture and Natural Resources, Cyprus

Markides, L., 1985, 1:25.000 Sheet 50&56 Kiti, Soil Section, Department of Agriculture, Ministry

of Agriculture and Natural Resources, Cyprus

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McBratney, A.B., Mendonça Santos, M.L., and Minasny, B.: On digital soil mapping. Geoderma

117, 3-52, 2003

Noller, J.: The Geomorphology of Cyprus. Cyprus Geological Survey, Open File Report, 269 p,

2009.

Saxton, K.E., and Rawls, W.J.: Soil water characteristic estimates by texture and organic matter for

hydrologic solutions. Soil Sci. Soc. Am. J. 70:1569–1578, 2006.

Soteriades C.and Georgiades, M., 1967, 1:25.000 Sheet 22 Kythrea, Soil Section, Department of

Agriculture, Ministry of Agriculture and Natural Resources, Cyprus

Soteriades C.and Grivas, 1968, 1:25.000 Sheet 20 Kokkinotrimithia, Soil Section, Department of

Agriculture, Ministry of Agriculture and Natural Resources, Cyprus

Soteriades, C., Koudounas, C, Markides, L., 1968, 1:25.000 Sheet 51 Paphos, Soil Section,

Department of Agriculture, Ministry of Agriculture and Natural Resources, Cyprus

Soteriades C.G., Koudounas C., 1968, Soils Memoirs of Pafos, Sheet no. 51, includes 1:25000 map,

Ministry of Agriculture and Natural Resources, Department of Agriculture, 96 p

Soteriades, C., Markides, L., 1969, 1:25.000 Sheet 44&45 Polemi, Soil Section, Department of

Agriculture, Ministry of Agriculture and Natural Resources, Cyprus