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Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1261
Mapping of Soil Geochemistry in Port
Said Governorate, Egypt Utilizing GIS
and Remote Sensing Techniques
Rana Y. El-Kady1, Ahmed E. El-Rayes
2, Yasser M. Sultan
3 &
Akram M. Aziz4
1,3,4 Geology Department, Faculty of Science, Port Said University, Port Said, Egypt
2 Geology Department, Faculty of Science, Suez Canal University, Ismailia, Egypt
Abstract: Port Said soil geochemistry is the major
soil limitation factor affecting agricultural
production. Ions content and soil salinity
distributions are increasingly needed, particularly
for better soil management. Fifty-sex samples were
taken with complete coverage of the study area at
depth of 40 cm. The cultivated areas are determined
utilizing satellite image of Landsat 8 by using NDVI
method. The chemical analysis for the soil extract
were done utilizing titration method for Cl, HCO3,
Ca and Mg ions, colorimeteric method for SO4 ion,
flame spectrophotometery for Na ion, TDS-meter for
TDS, electric conductivity meter for Ec. Sodium
Absorption Ratio (SAR) is empirically determined
using the chemical concentrations of Na, Ca, and
Mg. Utilizing Arc GIS, every ion concentration is
mapped to detect its spatial distribution in the study
area. The results show that the high concentration of
Calcium and Magnesium ions located south Malaha
Lake. The high concentrations of sodium and
chloride ions are located at the eastern part of El-
Salam Canal. The high concentrations of Ec, sulfate,
and TDS are located at restricted area between Suez
Canal and El-Salam Canal. The soil salinity
classification shows that areas south El-Tina Plain
classified as saline-sodic type, which needs extensive
treatment before cultivation.
Key Words : Geographic Information System,
Remote Sensing, Soil Geochemistry, soil mapping,
Port Said.
1. Introduction
In the last decades, the intensity of soil
degradation remarkably increases, particularly in the
Nile Delta region because of human activities [1] and
uncontrolled urbanization. Therefore, the need for
land reclamation in new areas appeared to
compensate the decreases of suitable soil areas for
agriculture. The present work aimed to delineate the
suitable zones for new agricultural expansions in
Port Said Governorate based on soil geochemistry.
Most soil reclamation faced increases of the salinity
and alkalinity, which became a major global issue.
The soil salinity mainly increases along coastal zones
impacted by sea water. The poor quality of
groundwater affects the chemistry of soil that hamper
the cultivation process. Remote sensing (RS) and
Geographic Information System (GIS) techniques
were extensively used for understanding soil
degradation processes and modeling soil degradation
risk [2] based on soil chemistry.
Port Said Governorate is one of the areas that newly
involved in the land reclamation program. It is
located at the northeastern part of Egypt, along with
the eastern side of the Nile Delta, which lies at the
most northern gate of Suez Canal on the
Mediterranean Sea [3], on a narrow peninsula
between the Manzala Lake and the Mediterranean
[4], which occupies an total area of 1464.21 km2 and
land area reach up to 889.1 Km2 (Fig.1).
Figure 1: Location map of Port Said Governorate.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1262
The study area is bounded by Latitudes
30°53'22.90"N & 31°21'49.86"N, and Longitudes
32°3'52.66"E & 32°33'16.30"E. It is characterized by
low relief and gently slopes towards the coastline of
Mediterranean. The south sector of the Governorate
was invaded by old branch of Nile known as Pelusiac
branch, which constitutes the main supplier of soil
that used for land reclamation process.
Generally, Port Said surface soil consists of four
classes of sediments (Fig. 2). Sabkha covers most of
the mapped area. Nile silt exists in mainly at the
northern sector around Port Said and part of Port
Fouad cities. The salt crust existed near Malaha Lake
to the northeastern sector. The Wadi and Playa
deposits are distributed as sand bars along the
southeastern parts and the western coast.
Figure 2: Distribution of surface soil sediments at Port
Said Governorate area (modified after [5]-[6].
El-Tina Plain and south Port Said city have
the most suitable soil for cultivation. El-Tina Plain
consider as an integral part of the ancient Nile Delta
sedimentation [7]. According to Hassan (2003) [8],
El-Tina Plain characterized as a triangular shape that
bordered from the west by the Suez Canal, from the
north by the Mediterranean coastline and from the
south by a sharp line contact with northern Sinai
sand sheet and ancient Pelusiac fault.
El-Tina Plain is a structural depression that
was filled by soil consists of extensive mud and
covered by salt crust in distant parts, mixed with
marine water [9] with 1 m to 3 m elevation above sea
level. The amount of new sediment reaching the
plain through the Nile River has been greatly reduced
over the last 40 years following the construction of
the Aswan high dam.
El-Tina Plain classified into two zones
separated by El-Salam Canal; a northern strand plain
and a southern delta plain [10]. The northern strand
plain width increases from 1 km in the east to 12.5
km in the west. It contains the Malaha Lake at the
northern part with a concave shoreline configuration
of about 39 km long and 818 km2 area [11]. The
southern part of the plain is composed of muddy
delta sediments [11]. It is also composed of sandy
plain sheet unit that occupies a narrow zone to the
east and southeast of Malaha Lake. The soil salinity
of the area varies from slightly saline to highly saline
[12]-[13].
2. Materials and methods
The most efficient tools to assess the spatial
integration of various data sets including geological
maps, Landsat 8 images, and soil chemistry data are
found in RS and GIS tools [14].
The methodological development over the
study area aims to show the concentration levels and
spatial distribution of chemical components and
salinization of Port Said soil by using ERDAS
Imagine and ESRI ArcGIS 10.2.2 software.
RS data are represented by cloud-free
Landsat 8 Operational Land Imager (OLI) imagery
with 11 band, which dated on the 14th of February
2015 with Path/Row (176/38) and (176/39) to apply
the Normalized Difference Vegetation Index (NDVI)
method. The spatial resolution is 30*30 m and
represented in the UTM WGS 1984 datum and Zone
36.
Many image processing is applied on the
satellite image bands include stack the bands in one
image layer and rectify the study area from the
satellite image.
The NDVI method is the indices ratio
images and classification techniques were applied to
provide information on vegetation distribution and
dynamics, calculate the areas used for cultivated
purpose and differentiate between the cultivated
zones, wetlands and water bodies of Port Said
Governorate. The green leaves have high visible light
absorption together with high near-infrared
reflectance, resulting in positive NDVI values. Bare
soil, cloud, and concrete have NDVI values close to
zero, while water has negative NDVI values [15].
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1263
In addition to tabular data, including chemical
characteristics of soil from, are obtained from
previous studies [16] and from field measurements
and laboratory experiments. The soil samples were
taken at 0.4 m depth. The sample location is
specified by using GPS device. The collected soil
samples were widely distributed over the entire Port
Said area. The surface soil samples were collected
manually in polyethylene bags. The soil chemical
analysis is focused on the determination of
Bicarbonate (HCO3-), Chloride (Cl
-), sulfate (SO4
2-),
Total Dissolved Salts (TDS), Sodium (Na+),
magnesium (Mg2+), calcium (Ca2
+), Sodium
Adsorption Ratio (SAR), and Electric Conductivity
(Ec). These ions are analyzed in soil extract using
titration method for HCO3, Ca, and Mg, flame
photometry for Na+, colorimetry for SO4
2- and by
electric conductivity meter for Ec.
The ion composition is expressed in
milliequivalents per litre (meq/l), which represents
the molar concentration of the ion, normalized by the
ionic charge, while Ec is measured in ds/m.
SAR is calculated using calcium, sodium and
magnesium concentrations according to the
following equation [17, 18].
The results of chemical analyses were integrated
with GIS database using attribute tables with
coordinates of each sample location.
3. Results and discussion
3.1. NDVI
The results of RS analyses of the study area
showed that the agricultural zones are concentrated
at the southeastern locality and at the zones confined
between west Suez Canal and Manzala Lake (Fig. 3)
El-Tina Plain considered as wetland zone, which
defined as zones of temporary filled with water [19].
The cultivated area occupies 280 km2 out of the total
area 1464.2 km2 of Port Said Governorate (Fig. 4).
Figure 3: Normalized Difference Vegetation Index
(NDVI) map of Port Said area.
Figure 4: Distribution of cultivated zones in Port Said
Governorate.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1264
3.2. Soil ions distribution
A number of 56 soil samples distributed
around the entire study area are collected and
subjected to chemical analysis for major ions (Fig.
5).
Figure 5: Soil samples-location map of Port Said area.
3.2.1. Calcium Ion Distribution
Calcium is the most predominant cation in soils.
The average calcium content of the earth's crust is
about 3.6% and total amount of calcium in the soil
ranges from less than 0.1% to as much as 25%.
The clayey soils usually contains more calcium
than sandy soils [20]. Calcium concentrations in soil
of the study area are ranged from 200 to 1800 meq/l
(Fig.6).
The calcium distribution map shows that the high
concentration values are recorded at two locations in
the eastern part of Port Said, near the Malaha Lake.
Generally, calcium might be supplied by several
ways. Gypsum might be the main source of calcium
when the soil pH is high. Other sources of calcium
include calcium nitrate (Ca (NO3)2), which contains
18-19.5% of Ca and also calcium chloride that
contains about 42% of Ca [20].
Figure 6: Calcium distribution map in soil of Port Said
Governorate.
3.2.2. Magnesium Ion Distribution
The obtained data of chemical components of soil
showed that the high magnesium contents are
distributed at the eastern parts of Port Said along two
localities to the south of Malaha Lake (Fig. 7).
Figure 7: Magnesium distribution map in soil of Port Said
Governorate.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1265
Generally, soil magnesium comes from
weathering of rocks containing biotite, hornblends
dolomite and chlorite minerals. The common source
rock for magnesium is dolomitic limestone, which
provide both calcium and magnesium, potassium –
magnesium sulfate, magnesium sulfate, magnesium
nitrate and magnesium oxide. It also found in soil
solution and is adsorbed to clay and organic matter
surfaces. The soils often contain less exchangeable
magnesium than calcium because magnesium not
absorbed as tightly by clay and organic matter and is
more subject to leaching [20].
3.2.3. Sodium Ion Distribution
Sodium ion concentrations in soil of Port Said
area are ranged from 100 to 2200 meq/l. Soil sodium
ion of the study area are concentrated at two
localities, at the southeastern and the southwestern
parts of Port Said along El-Salam Canal (Fig.8). It is
obvious that the source of sodium in soil of the study
area is the leakage from El-Salam Canal. It is noticed
that the sodium concentrations are decreases by
moving away from El-Salam Canal.
Figure 8: Sodium distribution in soil of Port Said
Governorate.
3.2.4. Chloride Ion Distribution
Chloride ion contents in soil of Port Said
area are ranged from 100 to 1500 meq/l. Chloride ion
in soil is concentrated mainly in the eastern part of
Port Said (Fig. 9).
Figure 9: Chloride distribution map in soil of Port Said
Governorate.
Both chloride and sodium concentrations have
nearly the same distributions away from the sea
water. This may attributed to the presence of halite
layer near the ground surface in that area (Fig.10).
The halite belongs to halide group that considered as
the most soluble minerals and easily to broken down
by physical and chemical weathering [21]. The halite
is found only in the salt-affected soils.
Figure 10: Halite layer at shallow depth of El-Tina plain.
3.2.5. Bicarbonate Ion Distribution
The excessive of bicarbonate concentration
adversely affects the absorption of ions and causes
chlorosis in plants and inhibit the metabolic process
of plant, which ultimately affect plant growth and the
uptake of nutrients [22].
Bicarbonate (HCO3) contents measured in
meq/l are ranged from 1 to 17 meq/l. Bicarbonate ion
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1266
in soil distributed in two localities at the western part
and southern parts of Port Said (Fig. 11).
Figure 11: Bicarbonate distribution map in soil of Port
Said Governorate.
3.2.6. Sulfate Ion Distribution
Sulfate (SO4) is measured in meq/l, are
ranged from 20 to 380 meq/l. High sulfate ion in soil
are distributed at south of Port Said along the
intersection of Suez canal with El-Salam Canal (Fig.
12). It has no major effect on the soil other than
contributing to the total salt content (TDS) [23].
In most cases, the high sulfate soil contains
gypsum mineral, which easily soluble. The gypsum
may found in soil of the study area as mixed granules
or as a thin layers.
Figure 12: Sulfate distribution map in soil of Port Said
Governorate.
3.2.7. Total Dissolved Salts (TDS) Distribution
Soil salinization is a universal problem,
especially in extensively irrigated areas that are
poorly drained or areas reused drained water in
irrigation. Soil salinity is typically assessed by
measuring the soil electrical conductivity (EC) in
saturated paste extracted from soil [24, 25]. The high
saline soils are distributed along Suez Canal and
southwest of Port Said area (Fig. 13). The TDS of
soil ranged from 40000 to 280000 meq/l. The TDS
level considered as very high, which exceeds the
salinity of the Mediterranean Sea water.
In general, the major sources of soluble salts
in soils are weathering of primary mineral and native
rocks, residual fossils salts, atmospheric deposition,
saline irrigation and drainage waters, saline
groundwater, sea water intrusion, additions of
inorganic and organic fertilizers, sludges and sewage
effluents, brines from natural salt deposits, and
brines from oil and gas fields and mining [26].
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1267
Figure 13: TDS distribution map of soil in Port Said
Governorate.
3.2.8. Electric Conductivity (Ec)
Soil electrical conductivity is one of the soil
important character as the preferred index to assess
soil salinity. Under standard condition, E increases as
salt concentration increase [26]. The soil Ec ranges,
are classified into five distinct classes of saline soils;
slightly affected, moderately affected, strongly
affected, very strongly affected and abnormally
affected, (Table 1)
Table 1: Soil electric conductivity classes and its effect on
salinity ([14, 27]).
EC Class Type EC Range (ds/m)
Slightly affected 4 – 8
Moderately affected 8 - 16
Strongly affected 16 – 32
Very strongly affected 32 - 64
Abnormally affected >64
Data showed a highly significant effect of soil
electrical conductivity in most of area at the
northeastern and the southwestern parts (Fig. 14),
which indicate strong effected while at the
southwestern part showed slightly effect.
The other Ec classification showed high
concentration along Suez Canal at the same location
of high concentration of TDS and sulfate (Fig. 15).
The Ec of alkali clay loam soil exhibits continuous
release of soluble salt with increasing the applied
sulfur [28].
Figure 14: Distribution of Ec effect on soil salinity
according to GARPAD (1984) Classification.
Figure 15: Distribution of Ec of Port Said soil.
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1268
3.2.9. Sodium Absorption Ratio (SAR)
SAR is a very important criteria to classify the
soil as sodic or non-sodic. Soil SAR depends upon
relative quantities of Na and Ca plus Mg in the soil
solution and clay complex [29]. The USDA (1954)
[17] classified the SAR as values of less than 13 and
more than 13, which integrated with Ec. Most of Port
Said soil have very low SAR value, while the area
with values less than 13 is located at the western
coast, central part of Port Said and southern part of
Port Said (Fig. 16).
Figure 16: SAR distribution at Port Said Governorate.
3.2.10. Sodium Absorption Salt (SAR) and
Electric Conductivity (EC)
The study area is mostly covered by
considered as saline-non sodic soil, which occupies
nearly the half of El-Tina Plain (Fig. 17). The
relative high soil SAR could be explained on the
basis of increased salt accumulation, which caused
precipitation of CaCO3 and CaSO4 like salts leading
to high Na then increase in SAR [29]. Also SAR
values are generally referenced to the level of
bicarbonate (HCO3)-. High concentrations of anions
can also increases soil salinity by affecting the
exchangeable sodium and calcium ratio [30]. When
soil moisture decreases, water soluble calcium
bicarbonate Ca(HCO3)2 decomposes and precipitates
calcium carbonate.
The sodic soils with high content of Na+ can
significantly alter some important soil physical and
chemical properties such as dispersion of soil
particles and poor soil water permeability. Soil
dispersion is the primary physical process associated
with high sodium concentration [31, 30] because the
attraction forces that bind clay particles can be
disrupted by high content of sodium ions causes
plugging of soil pores.
Upon repeated wetting and drying and
associated dispersion, soils reform and solidify into
cement-like soil with little or no aggregate formation
[32], which will significantly reduce soil infiltration,
hydraulic conductivity and lead to surface crusting.
As a result, the cement–like soil structure will
impede water flow or infiltration in the soil, which
will induce more surface runoff and soil erosion [33].
The ratio of salinity (Ec) to sodicity (SAR)
determines the effects of salts and sodium on soils,
which surrounding and effect on the foundation of
buildings.
Both of Ec and SAR coverage were
combined together in a mathematical manipulation
using GIS to assess various levels of salinity and
sodicity in study area that classify the soil for salt-
affect soils as shown in Table 2. The integration
between Ec and SAR shows highly effect of sodicity
and salinity at the southeastern part of Port Said
Governorate and around the western sector of El-
Salam Canal (Fig. 17).
Table 2: Classification of soil salinity and salt–affected soil [17, 14].
The increasing SAR of soil, which contain
magnesium salts, leads to dissolve sodium
hydroxide, cement, bricks and magnesium hydroxide
in addition to the attacking of sulfate compounds to
calcium and aluminum.
Class Ec (ds/m) SAR (meq/l)
Salt Free <4 <13
Saline-nonsodic >4 <13
Saline-sodic >4 >13
Nonsaline-sodic <4 >13
Imperial Journal of Interdisciplinary Research (IJIR)
Vol-3, Issue-3, 2017
ISSN: 2454-1362, http://www.onlinejournal.in
Imperial Journal of Interdisciplinary Research (IJIR) Page 1269
Figure 17: Distribution map of classified salt-affected soil
at Port Said according to USDA (1954) classes.
4. Conclusion
The present study assessed the soil salinity
based on the geochemical properties of the collected
samples from Port Said area. The Satellite images of
Landsat 8 was used to apply NDVI method to
delineate the cultivated areas of Port Said
Governorate. With the application of Arc GIS and
geostatistical mapping, the spatial distribution of soil
salinity and soil ions was mapped and evaluated
based on the grid sampling and laboratory
measurements. The normalized difference vegetation
index (NDVI) analysis showed that the cultivated
areas concentrated at the western part of Manzala
Lake and at southeastern part of Port Said
Governorate. Utilizing SAR equation, the salinity
evaluation showed that the main localities of soil
salinity was highly distributed across the
southeastern part of Port Said Governorate. The high
concentration of calcium and magnesium are
distributed at the southern part of Malaha Lake. The
high concentrations of sodium and chloride are
distributed at the eastern part of El-Salam Canal. The
high concentrations of Sulfate, total dissolved salts
(TDS), electric conductivity (EC) are found at the
intersection between El-Salam Canal and Suez
Canal. The high concentration of bicarbonate is
found at the southern part of Port Said City.
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