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International Journal of Trend in Scientific Research and Development (IJTSRD)
Volume 4 Issue 1, December 2019 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470
@ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 423
Analysis of Sand Dunes Accumulation using
Remote Sensing and GIS
Dr. Abdelrahim Elhag1, Dr. Nagi Zomrawi2, Sahar Khidir3
1Associate Professor of Surveying and GIS,
2Associate Professor of Surveying and Digital Mapping,
3Civil Engineer, SES Consultancy, Sudan
1,2Sudan University of Science and Technology, Khartoum, Sudan
ABSTRACT
Sand dunes is one of desertification phenomenon that hinder land resources
and human activities. It threaten to bury human settlement, roads, farms,
water and other resources. Due to many environmental and climate
conditions, there are many places around the world suffering from sand
movement and mobile dune creep onto cultivated land and human
settlements. Sand dunes have a fragile environment where, instability with a
series of changes lead to not equilibrium system with its surroundings within
an arid and hyper-arid climate changes. These changes usually characterized
by increase of evaporation and long periods of dryness, very low rainfall and
vegetation.
The aim of this research work is to applyremotesensing andGIStechniquesto
monitor and analyze sand dunes accumulation in the northern part of Sudan.
Three successive satellite images acquired in different dates have used as the
main source of data in this research work. A digital elevation model also
needed for topographic analysis. GIS has used to analyze output remote
sensing data.
Results reflected that, sand dines accumulated during the last years and its
accumulation in progress by 0.4% every year. Moreover, 50% of the study
area expected to be cover by sand dunes after less than 20 years. From
topographic point of view, sand dune heights reached be 20m. These results
present clear indicators of desertification that faces the study area.
KEYWORDS: Desertification, GIS, Landsat, NDVI, Remotesensing, Sanddunesand
TM
How to cite this paper: Dr. Abdelrahim
Elhag | Dr. Nagi Zomrawi | Sahar Khidir
"Analysis of Sand Dunes Accumulation
using Remote Sensing and GIS"
Published in
International
Journal of Trend in
Scientific Research
and Development
(ijtsrd), ISSN: 2456-
6470, Volume-4 |
Issue-1, December
2019, pp.423-427, URL:
https://www.ijtsrd.com/papers/ijtsrd29
507.pdf
Copyright © 2019 by author(s) and
International Journal ofTrendinScientific
Research and Development Journal. This
is an Open Access article distributed
under the terms of
the Creative
CommonsAttribution
License (CC BY 4.0)
(http://creativecommons.org/licenses/by
/4.0)
I. INRODUCTION
A sand dune is a mound of sand usually formed in windy
areas with very little or no vegetation and with lots of sand.
They created from drifting sand grains in a process called
saltation. As winds blow, the sand grains bounce on the wind
side surface until they reach the top of the mound. They,then
fall on the slip face side forming sand hills or sandduneswith
different shapes. Crescent, linear and star are the common
shapes of sand dunes.
Desertification experienced by about 40 % of global land
surface, which affects more than one billion people, half of
them living in Africa. Desertification is a form of land
degradation, occurring particularly in semi-arid areas, and
has been a major issue in the international agenda. Land
degradation leads to a decline in the land quality with a
negative impact on its capacity to function effectively within
an ecosystem by accepting, storing and recycling water,
energy, and nutrients.
The major desertification processes are wind erosion, water
erosion, denudation of vegetation cover while the other
minor ones include salinization, sodicity and compaction of
the soil.
The Sudanese Desert Encroachment Control and
Rehabilitation Programme (DECARP) declared that a
combination of factors cause desertification in Sudan. These
factors involve; fragileecosystemdevelopedunderharshand
fluctuating climate, and man’s activities. Some of which are
increased in an irreversible magnitude by weather
fluctuations especially periodic drought [5].
II. REMOTE SENSING AND GIS
Remote sensing is the scienceof acquiring informationabout
the earth's surface without actually being in contact with it.
This done by sensing and recording reflected or emitted
energy then, processing, analyzing, and applying that
information. In much of remote sensing, the processinvolves
an interaction between incident radiation and the targets of
interest. However, remote sensing also involves the sensing
of emitted energy and the use of non-imaging sensors [15].
A Geographic Information System (GIS)isacomputersystem
for capturing,storing,checking,anddisplayingdatarelatedto
positions on Earth’s surface.By relating seemingly unrelated
data. GIS can help better understanding spatial patterns and
relationships.
IJTSRD29507
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 424
Many different types of information can be compare and
contrasted using GIS. The system can include data about
people, landscape, and sites in both raster and vector forms.
Now days GIS used in every field to to make maps, perform
analysis, share information, and solve complex problems [13].
Remote sensing and GIS techniques can be use as a tool to
study dynamic features such as sand dunes and give a
synoptic view of the entire field as well as it sources. In
addition, the ability to examine changes over time allows for
the extrapolation of current climate regimes and the
monitoring of marginal areas susceptible to future
desertification.
III. STUDY AREA AND DATA COLLECTION
The Northern state is one of the eighteen states of Sudan. It
has an area of 348,765 km². It is characterised by an arid
environment with evapo-transpiration far exceeding the
very low average of rainfall per year. Because of the harsh
climatic conditions, the area becomes highly susceptible to
wind erosion, which lifts and transports the fine particles of
the dominant soils. Stronger winds remove the heavier
particles to form dunes, which endanger agricultural lands
and settlements. Over time, these processes lead to a
pronounced loss of productivity [13].
The study area of this resarch work is located in the
Northern State of Sudan between 18°35ʹN to 18°42ʹN
latitudes and 30°32ʹEto30°40ʹElongitudesasdemonstrated
in figure (1) below.
Fig.1: The study area
Data collected for this resarch work include three different
Landsat satellite images (Path 175 rows 47) covering the
study area with spatial resolution of 30 meters. Thefirst was
Landsat-7 TM image acquired in March, 2000; the second
was Landsat-7 TM image acquired in January 2007 where,
the third was Landsat-8 TM image acquired in March, 2018.
A Digital Elevation Model (DEM) with 30 meters resolution
was also obtained.
IV. DATA ANALYSIS
The raw Landsat satellite images files were first
uncompressed and combined in onefileusingErdasImagine
8.5. These images were then, reduced to WGS84 datum and
zone N 36 UTM projection. Subsets have also carried out in
order to extract images of the study area.
One of the powerful tools of Erdas package is that, theability
to use it to analyze successive images to detect changes and
monitor the sand dune migration in the studyarea.Thus,the
difference of satellite images acquired in dates 2000 and
2007 was carried out to detect changes occurred. Figure (2)
illustrates the obtained result.
Fig.2: Sand dunes change map 2000/2007
Again, changes have detected between image 2007 and
image 2018. Result of this difference illustrated in figure (3)
hereunder.
Fig.3: Sand dunes change map 2007/2018
From figure (2) and figure (3) above, it can obviously noted
how sand dines accumulated during the period.
In order to estimate the rate of encroachment of the sand
dunes within the study area, remote sensing analysis has
extended to determine the area that covered by sand dunes
in 2000 compared with 2007 and 2018. Figure (4)
represents the resultant image.
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 425
Fig.4: Successive changes in sand cover
From figure (4) above, yellow colour indicates areas of sand
cover in 2000. In 2007 sand, cover extended in larger areas
as indicated in violet. It is obvious that in 2018 sand dunes
much accumulated as shown in the red colour.
Usually, Landsat satellite based indices images produced to
portray the surface changes that happened during the study
period.
Changes in vegetation cover usually indicated by the
Normalized Difference VegetationIndex(NDVI)thatderived
from the ratio of band 3; Red (R) and band 4; Near Infra-Red
(NIR) of Landsat TM image data set. Where, NDVI= (NIR-R)/
(NIR+R).
Here, in this research work, the geometrically corrected
Landsat TM images band 3 and band 4 have used to derive
the vegetation Index.
NDVI has applied to that image acquired in year 2000 as
shown in figure (5) below.
Fig. 5: Normalized difference vegetation index (2000)
Figure (6) represented below, demonistrates the
normalized difference vegetation index in year (2018).
Fig. 6: Normalized difference vegetation index (2018)
A comparison between figure (5) and figure (6) reflectshwo
sand dunes extended where bare soil backing down.
Now, supervised classification has applied to the three
images. The classified images then entered as input data in
ArcGIS 10.1 software. Next, the extracted sand dunes zones
converted from raster to vector polygons. Sand dunes areas
have calculated from attribute tables and tabulated as listed
in table (1) below.
Table1: Increment of sand dunes areas
Date
Sand area
(Km2)
Increment
(Km2)
Increment
/year (Km2)
2000 3.7 - -
2007 20.0 16.3 2.3
2018 55.5 35.5 3.2
From table (1) above, it can be seen that, sand dunes
acuumulated by 16.3 km2 during the period 2000to2007by
rate of 2.3 km2 per year. On the other hand, accumulation
rate was 3.2 km2 per year during the period from 2007 to
2018 i.e. sand dunes accumulation rate increase last years.
Now, representing years against sand dunes areas, second
order polynomial trend line equation has approximated as
follows:
y = 9.6x2 - 12.5x + 6.6 … (1)
Where,
x representing years
y is the expected sand dunes areas
This implies that after less than 20 years, 50% of the study
area will be covered by sand dunes. Figure (7) below
illustrates sand dunes areas and the trend line.
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 426
Fig. 7: Sand dunes areas and trend line
Study area covers about 250 km2. Comparing accumulation
rate with the whole study area yields 0.9%duringtheperiod
2000 to 2007. This rate was increaed to be 1.3 during the
period 2007 to 2018. This result idicate that accumulation
rate increse by 0.4% every year.
Table2: Rate of increment
Date
Increment
/year (Km2)
Incement
Per year
%
Rate of
increment %
2000 - -
0.42007 2.3 0.9
2018 3.2 1.3
Sand dunes heights have also examined in this study. A
topographic map was prepared for the study area using GIS
by creating contour map from the data of the digital
elevation model as appeared in figure (8).
Fig.8: Topographic map of study area in year 2018
Now, a profile graph for a sample area havecreatedandsand
dune height measured to be 20m as figure (9) illustrates.
Fig. 9: Profile graph of a sample area
Since this sample randomly selected, it can expect to find
dunes higher than 20m.
V. CONCLUSION
In those areas facing desertification, it is almostnecessaryto
plan for comprehensiveprogramforsandstabilization.Since
the study area fall on such desertification progress, urgent
percussions would be took into consideration.
From the data collected about study area and analysis
carried out it can be conclude with the following points:
Sand dines accumulated on the study area during the
last period and its accumulation in progress.
NDVI analysis reflected that sand dunes increase while
bare soil decrease.
Sand dunes accumulations increased by 14%
throughout the last 18 years.
Sand dunes accumulation rate increases by 0.4% every
year.
Sand dune height reached 20m in thestudyarea.Where,
higher than 20m can be expected.
Fifty percent of the study area expected to be cover by
sand dunes after less than 20 years.
These factors imminent threat of desertification that
faces the study area thus, urgent intervention neededby
implementing adequate methods.
Remote sensing and GIS are successful tools in sand
dunes monitoring.
REFERENCES
[1] Prof. Dr. H. J. Herrmann &Prof. Dr. M.Fahnle,Vegetated
dunes and barchan dune fields, 29. January 2007
[2] Michael J. Kavulich Jr., Degree of Bachelor of Science in
Physics (April 27, 2008), Faculty of the worcester
polytechnic institute, a major qualifyingprojectreport.
International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470
@ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 427
[3] National Geographic Society, A. Strahler, O.W.
Archibold, Physical Geography: ScienceandSystemsof
the
[4] Human Environment, 2008. John Wiley & Sons, pag.
442
[5] Dafalla M.S., Ibrahim S.I., Elhag A.M.H and Doka, M.A.2,
Assessment of Sand Encroachment Using Remote
Sensing and GIS, University of Khartoum.
[6] Lahmeyer international, sand stabilization study,
Merwe Irrigation project.
[7] Han Qing-jie, QuJian-jun, Liao Kong-tai, Zhu Shu-juan,
Dong Zhi-bao, Zhang Ke-cun and ZuRui-ping, A Wind
Tunnel Experiment of Aeolian Sand Transport over
Wetted Coastal Sand Surface, Journal of Desert
Research, Volume 32, Issue 6, 2012, Pages 1512-1521.
[8] Amelia Carolina Sparavigna,A study of moving sand
dunes by means of satellite images, Department of
Applied Science and Technology, PolitecnicodiTorino,
Italy.
[9] Ramsey, M. S. (2003) Global Desert Monitoring With
ASTER; Research Projects, IVIS Laboratory, University
of Pittsburg.
[10] Coppin, P. & Bauer, M. (1996) Digital Change Detection
in Forest Ecosystems with Remote Sensing Imagery.
Remote Sensing Reviews.Vol.13, pag.207-234.
[11] Ayad M. Fadhil Al-Quraishi , University Of Kufa , Sand
dunes monitoring using remote sensing and GIS
techniques for some sites in Iraq.
[12] Generic environmental impact statement sand dune
mining, MI DEQGSD - Generic EIS Sand Dune Mining -
GEIS.PDF
[13] https://en.wikipedia.org/wiki/Northern_state,_Sudan
[14] https://www.esri.com/en-us/what-is-gis/overview
[15] https://www.nationalgeographic.org/encyclopedia/ge
ographic-information-system-gis/
[16] https://www.nrcan.gc.ca/maps-tools-
publications/satellite-imagery-air-photos/remote-
sensing-tutorials/fundamentals-remote-sensing-
introduction/

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Analysis of Sand Dunes Accumulation using Remote Sensing and GIS

  • 1. International Journal of Trend in Scientific Research and Development (IJTSRD) Volume 4 Issue 1, December 2019 Available Online: www.ijtsrd.com e-ISSN: 2456 – 6470 @ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 423 Analysis of Sand Dunes Accumulation using Remote Sensing and GIS Dr. Abdelrahim Elhag1, Dr. Nagi Zomrawi2, Sahar Khidir3 1Associate Professor of Surveying and GIS, 2Associate Professor of Surveying and Digital Mapping, 3Civil Engineer, SES Consultancy, Sudan 1,2Sudan University of Science and Technology, Khartoum, Sudan ABSTRACT Sand dunes is one of desertification phenomenon that hinder land resources and human activities. It threaten to bury human settlement, roads, farms, water and other resources. Due to many environmental and climate conditions, there are many places around the world suffering from sand movement and mobile dune creep onto cultivated land and human settlements. Sand dunes have a fragile environment where, instability with a series of changes lead to not equilibrium system with its surroundings within an arid and hyper-arid climate changes. These changes usually characterized by increase of evaporation and long periods of dryness, very low rainfall and vegetation. The aim of this research work is to applyremotesensing andGIStechniquesto monitor and analyze sand dunes accumulation in the northern part of Sudan. Three successive satellite images acquired in different dates have used as the main source of data in this research work. A digital elevation model also needed for topographic analysis. GIS has used to analyze output remote sensing data. Results reflected that, sand dines accumulated during the last years and its accumulation in progress by 0.4% every year. Moreover, 50% of the study area expected to be cover by sand dunes after less than 20 years. From topographic point of view, sand dune heights reached be 20m. These results present clear indicators of desertification that faces the study area. KEYWORDS: Desertification, GIS, Landsat, NDVI, Remotesensing, Sanddunesand TM How to cite this paper: Dr. Abdelrahim Elhag | Dr. Nagi Zomrawi | Sahar Khidir "Analysis of Sand Dunes Accumulation using Remote Sensing and GIS" Published in International Journal of Trend in Scientific Research and Development (ijtsrd), ISSN: 2456- 6470, Volume-4 | Issue-1, December 2019, pp.423-427, URL: https://www.ijtsrd.com/papers/ijtsrd29 507.pdf Copyright © 2019 by author(s) and International Journal ofTrendinScientific Research and Development Journal. This is an Open Access article distributed under the terms of the Creative CommonsAttribution License (CC BY 4.0) (http://creativecommons.org/licenses/by /4.0) I. INRODUCTION A sand dune is a mound of sand usually formed in windy areas with very little or no vegetation and with lots of sand. They created from drifting sand grains in a process called saltation. As winds blow, the sand grains bounce on the wind side surface until they reach the top of the mound. They,then fall on the slip face side forming sand hills or sandduneswith different shapes. Crescent, linear and star are the common shapes of sand dunes. Desertification experienced by about 40 % of global land surface, which affects more than one billion people, half of them living in Africa. Desertification is a form of land degradation, occurring particularly in semi-arid areas, and has been a major issue in the international agenda. Land degradation leads to a decline in the land quality with a negative impact on its capacity to function effectively within an ecosystem by accepting, storing and recycling water, energy, and nutrients. The major desertification processes are wind erosion, water erosion, denudation of vegetation cover while the other minor ones include salinization, sodicity and compaction of the soil. The Sudanese Desert Encroachment Control and Rehabilitation Programme (DECARP) declared that a combination of factors cause desertification in Sudan. These factors involve; fragileecosystemdevelopedunderharshand fluctuating climate, and man’s activities. Some of which are increased in an irreversible magnitude by weather fluctuations especially periodic drought [5]. II. REMOTE SENSING AND GIS Remote sensing is the scienceof acquiring informationabout the earth's surface without actually being in contact with it. This done by sensing and recording reflected or emitted energy then, processing, analyzing, and applying that information. In much of remote sensing, the processinvolves an interaction between incident radiation and the targets of interest. However, remote sensing also involves the sensing of emitted energy and the use of non-imaging sensors [15]. A Geographic Information System (GIS)isacomputersystem for capturing,storing,checking,anddisplayingdatarelatedto positions on Earth’s surface.By relating seemingly unrelated data. GIS can help better understanding spatial patterns and relationships. IJTSRD29507
  • 2. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 424 Many different types of information can be compare and contrasted using GIS. The system can include data about people, landscape, and sites in both raster and vector forms. Now days GIS used in every field to to make maps, perform analysis, share information, and solve complex problems [13]. Remote sensing and GIS techniques can be use as a tool to study dynamic features such as sand dunes and give a synoptic view of the entire field as well as it sources. In addition, the ability to examine changes over time allows for the extrapolation of current climate regimes and the monitoring of marginal areas susceptible to future desertification. III. STUDY AREA AND DATA COLLECTION The Northern state is one of the eighteen states of Sudan. It has an area of 348,765 km². It is characterised by an arid environment with evapo-transpiration far exceeding the very low average of rainfall per year. Because of the harsh climatic conditions, the area becomes highly susceptible to wind erosion, which lifts and transports the fine particles of the dominant soils. Stronger winds remove the heavier particles to form dunes, which endanger agricultural lands and settlements. Over time, these processes lead to a pronounced loss of productivity [13]. The study area of this resarch work is located in the Northern State of Sudan between 18°35ʹN to 18°42ʹN latitudes and 30°32ʹEto30°40ʹElongitudesasdemonstrated in figure (1) below. Fig.1: The study area Data collected for this resarch work include three different Landsat satellite images (Path 175 rows 47) covering the study area with spatial resolution of 30 meters. Thefirst was Landsat-7 TM image acquired in March, 2000; the second was Landsat-7 TM image acquired in January 2007 where, the third was Landsat-8 TM image acquired in March, 2018. A Digital Elevation Model (DEM) with 30 meters resolution was also obtained. IV. DATA ANALYSIS The raw Landsat satellite images files were first uncompressed and combined in onefileusingErdasImagine 8.5. These images were then, reduced to WGS84 datum and zone N 36 UTM projection. Subsets have also carried out in order to extract images of the study area. One of the powerful tools of Erdas package is that, theability to use it to analyze successive images to detect changes and monitor the sand dune migration in the studyarea.Thus,the difference of satellite images acquired in dates 2000 and 2007 was carried out to detect changes occurred. Figure (2) illustrates the obtained result. Fig.2: Sand dunes change map 2000/2007 Again, changes have detected between image 2007 and image 2018. Result of this difference illustrated in figure (3) hereunder. Fig.3: Sand dunes change map 2007/2018 From figure (2) and figure (3) above, it can obviously noted how sand dines accumulated during the period. In order to estimate the rate of encroachment of the sand dunes within the study area, remote sensing analysis has extended to determine the area that covered by sand dunes in 2000 compared with 2007 and 2018. Figure (4) represents the resultant image.
  • 3. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 425 Fig.4: Successive changes in sand cover From figure (4) above, yellow colour indicates areas of sand cover in 2000. In 2007 sand, cover extended in larger areas as indicated in violet. It is obvious that in 2018 sand dunes much accumulated as shown in the red colour. Usually, Landsat satellite based indices images produced to portray the surface changes that happened during the study period. Changes in vegetation cover usually indicated by the Normalized Difference VegetationIndex(NDVI)thatderived from the ratio of band 3; Red (R) and band 4; Near Infra-Red (NIR) of Landsat TM image data set. Where, NDVI= (NIR-R)/ (NIR+R). Here, in this research work, the geometrically corrected Landsat TM images band 3 and band 4 have used to derive the vegetation Index. NDVI has applied to that image acquired in year 2000 as shown in figure (5) below. Fig. 5: Normalized difference vegetation index (2000) Figure (6) represented below, demonistrates the normalized difference vegetation index in year (2018). Fig. 6: Normalized difference vegetation index (2018) A comparison between figure (5) and figure (6) reflectshwo sand dunes extended where bare soil backing down. Now, supervised classification has applied to the three images. The classified images then entered as input data in ArcGIS 10.1 software. Next, the extracted sand dunes zones converted from raster to vector polygons. Sand dunes areas have calculated from attribute tables and tabulated as listed in table (1) below. Table1: Increment of sand dunes areas Date Sand area (Km2) Increment (Km2) Increment /year (Km2) 2000 3.7 - - 2007 20.0 16.3 2.3 2018 55.5 35.5 3.2 From table (1) above, it can be seen that, sand dunes acuumulated by 16.3 km2 during the period 2000to2007by rate of 2.3 km2 per year. On the other hand, accumulation rate was 3.2 km2 per year during the period from 2007 to 2018 i.e. sand dunes accumulation rate increase last years. Now, representing years against sand dunes areas, second order polynomial trend line equation has approximated as follows: y = 9.6x2 - 12.5x + 6.6 … (1) Where, x representing years y is the expected sand dunes areas This implies that after less than 20 years, 50% of the study area will be covered by sand dunes. Figure (7) below illustrates sand dunes areas and the trend line.
  • 4. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 426 Fig. 7: Sand dunes areas and trend line Study area covers about 250 km2. Comparing accumulation rate with the whole study area yields 0.9%duringtheperiod 2000 to 2007. This rate was increaed to be 1.3 during the period 2007 to 2018. This result idicate that accumulation rate increse by 0.4% every year. Table2: Rate of increment Date Increment /year (Km2) Incement Per year % Rate of increment % 2000 - - 0.42007 2.3 0.9 2018 3.2 1.3 Sand dunes heights have also examined in this study. A topographic map was prepared for the study area using GIS by creating contour map from the data of the digital elevation model as appeared in figure (8). Fig.8: Topographic map of study area in year 2018 Now, a profile graph for a sample area havecreatedandsand dune height measured to be 20m as figure (9) illustrates. Fig. 9: Profile graph of a sample area Since this sample randomly selected, it can expect to find dunes higher than 20m. V. CONCLUSION In those areas facing desertification, it is almostnecessaryto plan for comprehensiveprogramforsandstabilization.Since the study area fall on such desertification progress, urgent percussions would be took into consideration. From the data collected about study area and analysis carried out it can be conclude with the following points: Sand dines accumulated on the study area during the last period and its accumulation in progress. NDVI analysis reflected that sand dunes increase while bare soil decrease. Sand dunes accumulations increased by 14% throughout the last 18 years. Sand dunes accumulation rate increases by 0.4% every year. Sand dune height reached 20m in thestudyarea.Where, higher than 20m can be expected. Fifty percent of the study area expected to be cover by sand dunes after less than 20 years. These factors imminent threat of desertification that faces the study area thus, urgent intervention neededby implementing adequate methods. Remote sensing and GIS are successful tools in sand dunes monitoring. REFERENCES [1] Prof. Dr. H. J. Herrmann &Prof. Dr. M.Fahnle,Vegetated dunes and barchan dune fields, 29. January 2007 [2] Michael J. Kavulich Jr., Degree of Bachelor of Science in Physics (April 27, 2008), Faculty of the worcester polytechnic institute, a major qualifyingprojectreport.
  • 5. International Journal of Trend in Scientific Research and Development (IJTSRD) @ www.ijtsrd.com eISSN: 2456-6470 @ IJTSRD | Unique Paper ID – IJTSRD29507 | Volume – 4 | Issue – 1 | November-December 2019 Page 427 [3] National Geographic Society, A. Strahler, O.W. Archibold, Physical Geography: ScienceandSystemsof the [4] Human Environment, 2008. John Wiley & Sons, pag. 442 [5] Dafalla M.S., Ibrahim S.I., Elhag A.M.H and Doka, M.A.2, Assessment of Sand Encroachment Using Remote Sensing and GIS, University of Khartoum. [6] Lahmeyer international, sand stabilization study, Merwe Irrigation project. [7] Han Qing-jie, QuJian-jun, Liao Kong-tai, Zhu Shu-juan, Dong Zhi-bao, Zhang Ke-cun and ZuRui-ping, A Wind Tunnel Experiment of Aeolian Sand Transport over Wetted Coastal Sand Surface, Journal of Desert Research, Volume 32, Issue 6, 2012, Pages 1512-1521. [8] Amelia Carolina Sparavigna,A study of moving sand dunes by means of satellite images, Department of Applied Science and Technology, PolitecnicodiTorino, Italy. [9] Ramsey, M. S. (2003) Global Desert Monitoring With ASTER; Research Projects, IVIS Laboratory, University of Pittsburg. [10] Coppin, P. & Bauer, M. (1996) Digital Change Detection in Forest Ecosystems with Remote Sensing Imagery. Remote Sensing Reviews.Vol.13, pag.207-234. [11] Ayad M. Fadhil Al-Quraishi , University Of Kufa , Sand dunes monitoring using remote sensing and GIS techniques for some sites in Iraq. [12] Generic environmental impact statement sand dune mining, MI DEQGSD - Generic EIS Sand Dune Mining - GEIS.PDF [13] https://en.wikipedia.org/wiki/Northern_state,_Sudan [14] https://www.esri.com/en-us/what-is-gis/overview [15] https://www.nationalgeographic.org/encyclopedia/ge ographic-information-system-gis/ [16] https://www.nrcan.gc.ca/maps-tools- publications/satellite-imagery-air-photos/remote- sensing-tutorials/fundamentals-remote-sensing- introduction/