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INTERNATIONALJOURNALOF GEOMATICSANDGEOSCIENCES
Volume2,No 1,2011
©Copyright2010AllrightsreservedIntegratedPublishingservices
Researcharticle ISSN0976 –4380
SubmittedonJuly2011publishedonSeptember201121
Monitoringdesertificationrisk throughclimatechangeandhuman
interferenceusingRemotesensingandGIStechniques
ArnabKundu
1
,DipanwitaDutta
2
1CentrefortheStudyofRegionalDevelopment,SchoolofSocialSciences,Jawaharlal
NehruUniversity,NewDelhi110067,India.
2IndianInstituteofRemoteSensing,DepartmentofSpace,IndianSpaceResearch
Organisation,Dehradun248001,Uttarakhand,India.
arnknd@live.in
ABSTRACT
Thethreatofglobalclimatechangehasradicallyincreasedtheattentiondirectedtowards
understanding the effect on environment and its natural and human induced changes.
Climatic conditions along with certain human activities such as improper agricultural
practices, violent use of fertilizers, overgrazing and other unsustainable practices have
acceleratedtheconversionoffertilelandsintoaridlandsandthiseventuallyleadstoland
degradation and desertification. Theterm “desertification” indicates land degradation in
arid, semiarid and dry subhumid areas resulting from climate variations and human
activity. Stable degradation of vegetation cover is one of the basic characteristics of
desertification process. Changes in vegetation cover of the Churu district of Western
Rajasthanareveryclearlydetectedfromlongtermsatellitedataandithasbeenusedfor
monitoringdesertificationprocess.Inthispaper,longtermNOAAAVHRR(19832003)
data has been used to monitor desertification processes through NDVI timetrend. The
studyisbasedontheanalysisofregionallongtermchangesofvegetationconditionsthat
indicates the ongoing desertification processes. Vegetation growth is entirely depended
uponrainfall.Here,longtermNDVItrendhasbeenanalysedcorrespondingwiththelong
termannualrainfall(19832003).Itidentifiestheareasaffectedbydesertificationprocess
as a circumstance of climate change. The results confirmed that some parts of Churu
districtisunderclimaticallyinduceddesertificationprocesses.
Keywords: Climate change, Land Degradation, Desertification, Vegetation cover,
NOAAAVHRRNDVI,Rainfall.
1.Introduction
According to Adger et al., (2000) over 250 million people are directly affected by
desertificationandsomeonebillionpeopleinover100countriesareatrisk.India,being
oneofthe leadingdevelopingcountriesof theworld is notexemptedfromtheproblem
related to various natural hazards. Among them,desertification hase merged as a major
economic,socialandenvironmentalprobleminwestern partofIndia.The"GreatIndian
Desert" or Thar, located in Western India, is surrounded by Indus plains in the west,
Aravalli Range in the southeast, Rann of Kutch in the south, and Punjab plains in the
north and northeast. About 91% of the desert, i.e. 2.08 million square km falls in
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InternationalJournalofGeomaticsandGeosciences
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Rajasthanwhichcoverabout61%ofthegeographicalareaoftheRajasthan(Sinhaetal.,
2000). Encroachment of the Thar Desert towards its Eastern boarder has become a
seriousproblemtothe adjoiningdistrictsofthedesert. Itisslowlycapturingthe arable
lands by reducing their productivity. A large number of population and animals of this
region are at risk due to shifting of sand dunes, dust storms and as a consequence
decreasing agricultural productivity. To handle the desertification problem, various
programmes were undertaken by Govt. of India. As for example, Desert Development
Program (DDP) started in197778 with the objectives to control desertification, restore
the ecological balance of desert and semidesert areas and create conditions for raising
thelevelofproduction,incomeandemploymentofthepopulationoftheseareas.Inspite
ofseveralattemptstakenbyour Government,thereislackofwellplannedmanagement
and actual information on climate and human induced desertification. It is true that
climateinduceddesertificationisinevitableanddifficulttoprevent.But,itispossibleto
identify the areas exposed to desertification processes and that would be useful for
makingastrategytopreventtheexpansionofthedesert.Differentmethodsofevaluating
desertification include the use of direct observation and measurement, mathematical
models and parametric equation, estimates, remote sensing and indicators (Rubio and
Bochet, 1998). Nowa days, Remote Sensing is the most successful approach for
detecting the long term desertification process and vegetation changes. It is crucial to
identify suitable indicators for monitoring desertification at local, regional and global
scale.TheimportanceofindicatorsinmonitoringdesertificationwasrecognizedbyFAO
and UNEP in the year of 1980 and they proposed 22 indicators in the Provisional
Methodologyfor Assessment andMappingofDesertification.LipingDi,(2003) madea
detailedstudyonrecentprogressofremotesensingonmonitoringofdesertificationand
mentioned that remote sensing is the only tool of choice for desertification studies at
regionalandglobalscale.Remotesensinghasbeensuccessfullyappliedtotheprocessof
monitoring desert expansion and to the assessment of factors that cause desertification
(Hananetal.,1991).Thereisadistincteffectofdesertificationonvegetationcover.The
decreasing trend in vegetation cover indicates the ongoing desertification process in an
area. The Normalized Difference Vegetation Index derived from the long term NOAA
AVHRRdataisanestablishedtechniquefor monitoringlongtermchangesinvegetation
cover.TheNDVIanditsrelationtogreenbiomasswasfirstsuggestedanddemonstrated
byRouseet al., (1973)andTucker(1979).It is one ofthemost widelyused vegetation
indexanditsutilityinsatelliteassessmentandmonitoringofglobalvegetationcoverhas
been well exploited over the past two decades (Huete and Liu, 1994; Leprieur et al.,
2000).Inhisstudy,Zhang(1999)founda strongcorrelation(R
2
=0.73)betweenNOAA
AVHRRNDVIandVegetationcover.Thepresentstudyattemptstoinvestigatetheareas
experiencinglongtermdegradationofvegetationcoverresponsetoclimatechangeinthe
district, Churu. Here, two indicators of desertification have been selected to identify
climateinduceddesertification,oneislongtermrainfallandtheotherisremotesensing
basedindicatorNDVI.
2.Studyarea
The district Churu, situated in the eastern part of the Thar Desert occupies 13,740.95
square kilometres area which is about 12.40 percent of Indian Arid lands exposed to
different forms of desertification processes. It consists of six tehsils namely Sujangarh,
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Ratangarh, Sardarshahar, Churu, Rajgarh and Taranagar. The district is geographically
located in between 27
◦
24’ North to 29
◦ North latitude and 73
◦
51’49” East to 75
◦
40’
20”East longitude (Figure 1). It is enclosed by Mahendragarh and Hissar districts of
Haryana towards east; Hanumangarh district towards north; Nagaur, Sikar and Nagaur,
Sikar and Jhunjhunu districts towards south and south east; and Bikaner in the west.
According to Census of India (2001), the district has 7 towns, 908 villages and a total
populationof19,22,908personswithadensityof123peoplepersquarekm.Thedistrict
encompasses large shifting sand dunes andhas a varying altitude of213 to 400 meters
aboveMeanSeaLevel.
Figure1:StudyArea
Note:DungargarhtehsilisnowadjoinedwithBikanerdistrictofRajasthan
The surface is generally sloping from south towards North and is characterised by
isolated hills which are typical monadnocks on the former peneplain (Sidddiqui, A.R.,
2009).Climaticallytheregionbelongstohyperaridtypeofclimatewithhighdiurnaland
annual range of temperature, scanty rainfall, dry scorching winds and low relative
humidityresultinghigherrateofevaporation.Thiskindofclimatefuelsingeneratingand
transportingofloosesandordustparticles.Theregionrecordstemperaturerangingfrom
below freezing point in the winters to over 50 degrees in the summer afternoons. The
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InternationalJournalofGeomaticsandGeosciences
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pattern of rainfall varies spatially; it increases from West to East. The district is
characterizedbysandyto sandyloamcalcareous typeofsoilwhichiscoarse intexture,
lessstructuredwithnegligibleamountoforganicmatter.Asaresultofit,thesubsurface
percolation rate of soil has become higher and the water holding capacity of the soil
profiles have become low (Sidddiqui, A.R., 2009). The spatial pattern of vegetation
shows a great influence of spatial pattern of precipitation over here. Though there is a
poorvegetationcover,theareatowardseastisgreenerthanwest.Largeareasarecovered
with thorny scrubs, grasses with isolated trees. The scarcity of vegetation covers is
strengtheningtheAeolianprocessesandmakingthesanddunesmobile.Theeconomyof
Churuismainlybasedonagricultureandanimalhusbandry.Themajorcropsareoilseeds,
Wheat,Jowar(Sorghum),kharifpulsesandbajra(pearlmillet).
3. MaterialsandMethod
3.1NDVIData
TheNDVIisagoodindicatorofgreenbiomass,leafareaindexandpatternofproduction
(Thinkableetal.2004).Thefundamentalbehindthisindexisthattheinternalmesophyll
structureofhealthygreenleavesstronglyreflectsNIRradiationandleafchlorophylland
otherpigmentsabsorba largeproportionoftheredVISradiation.Thisbecomesreverse
incase ofunhealthyor waterstressed vegetation.NDVI iscalculated bythedifference
betweenreflectanceinnearinfrared(NIR)andvisiblered(VIS)bandofelectromagnetic
spectrum.
NDVI=(NIR−VIS)/(NIR+VIS)
The NDVI value variesbetwee n1.0 to +1.0. Itranges from 0.1 in deserts upto 0.8 in
densetropicalrainforest.TheValuesbetween0and0.1denotesrocksandbaresoiland
less than 1 indicate iceclouds, waterclouds, and snow. The NDVI has been used for
descriptionofcontinentallandcover, vegetationclassificationandvegetationphenology
(Tucker et al. 1985, Tarpley et al. 1984). NDVI derived from Advance Very High
Resolution Radiometer (AVHRR) onboard NOAA is much used for monitoring
vegetation growth and health and assessing desertification (Prince and Justice, 1991;
Tuckeretal.,1991;Nicholsonetal.,1998;Princeetal.,1998;DioufandLambin,2001;
Anyamba and Tucker, 2005; Olsson et al., 2005). NDVI is calculated from channel
1(visible) andc hannel 2(infrared) of AVHRR. In thisst udy, fortnightly GIMMS NDVI
fromNOAA(AVHRR)hasbeenusedforatimeperiodof21years(1983– 2003).This
datawascollectedfromtheNationalOceanicand AtmosphericAdministration(NOAA)
satellitewhichholdsthe AdvancedVeryHighResolutionRadiometer (AVHRR)sensor
andprimarilyoperatedbyUSA.Thesesensorscollecttheglobaldataonadailybasisfor
amultiplicityof land,ocean,andatmosphericapplications.Besidesthese,itisalsoused
to monitor forest fire, analysis of vegetation, weather forecasting, climatic condition,
study of drought, measurement of global sea surface temperature and ocean related
research.TheNDVIisconsideredasa‘greenness’indexinstudiesofdrylandvegetation
cover. It has found that in arid and semiarid regions, NDVI is well correlated with
parameterssuchas leafareaindex,Greenleaf,biomass,vegetationcover,etc.(Nicholson
et al., 1998). In his study, Zhang (1999) also found a strong correlation (R
2
=0.73)
betweenNOAAAVHRRNDVIandVegetationcover.
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Table1: CharacteristicsofNOAAAVHRRsensor
Characteristics NOAAAVHRR
InclinationofOrbit 98.922º
Heightabovesurface 851Km
Numberoforbits/day 14.1
Timesofcoverageatequator
01:41Descending
13:41Ascending
OrbitalPeriod 102min
LatitudinalCoverage 90ºN90ºS
CycleDuration 1Day
GroundCoverage 2842Km
FieldofView(FOV) ±55.4º
InstantaneousFieldofView(IFOV 1.391.51mrad
GroundResolution(Nadir) 1.1Km
NumberofChannels
OneVisible(0.50.7um)
OneNearInfrared(0.71.1um)
OneMiddleInfrared
TwoThermalInfrared
The NDVI data was freely downloaded from the University of Maryland Global Land
Cover Facility Data Distribution Centre (http://www.glcf.umiacs.umd.edu/data/gimms/).
The images were processed by theG lobal InventoryModelling andMo nitoring System
(GIMMS)groupatNASA’sGoddard Space FlightCentre.Forthisresearch,fortnightly
NDVI data was gathered from already processed 15day NDVI composites using the
maximum value compositing procedure to minimize effects of cloud contamination,
varyingsolar zenithanglesand surface topography(Holben, 1986).The Preprocessing
of 15 day composite GIMMSNDVI (1983 – 2003) data was carried out through
followingsteps:
1. ConversionfromGEOtiffformatto.imgformat
2. LayerStacking
3. Reprojection
4. Scaling
5. Subset
TheGIMMS NDVI dataisavailableinGEOtiffformatwhichwerefirstconvertedinto
image format. Then this 15 day composite dataset of 21 years (19832003) has been
stacked. Each stacked layer of all years encloses ten layersrepresenting ten fortnights
(JuneOctober) of growing season. These stacked layers were then reprojected into
AlbersEqualArea ProjectionwithWGS84 datum.Thisprojectionwas chosento keep
the similar pixel size. The following projection parameters are given for Albers Equal
Area Projection for India. Theser eprojected images wererescaled to retain theNDVI
valuerangingfrom+1to1usingthescalefactor0.001.
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ParametersusedforAlbersEqualAreaProjection:
1. SpheroidName:WGS84
2. DatumName:WGS84
3. Latitudeof1stStandardParallel:12ºN
4. Latitudeof2ndStandardParallel:28ºN
5. LongitudeofCentralMeridian:78ºE
6. Latitudeoforiginofprojection:20ºN
7. FalseEastingatcentralmeridian:2000000.0mts.
8. FalseNorthingatorigin:2000000.0mts.
3.2RainfallData
Longterm (19832003) monthly Rainfall data from India Meteorological Department
(IMD) were usedin this study. Monthly rainfall data of growing season( JuneOctober)
were collected from different rain gauge stations scattered in and around of the Churu
district. The rainfall of different months of growingseaso n was thena veraged for each
raingaugestationtoobtainthemeanrainfallofgrowingseason.
3.3Methodology
Thestudywascarriedout aimingto agoaltoidentifyareasundergoingclimateinduced
desertificationprocessesthroughremotesensingbasedindicatorNDVIandclimatebased
indicator rainfall. The data was processed to make it ready for further geostatistical
analysis. After preprocessing of the AVHRRNDVI images (19832003), they were
normalized for regression analysis. The normalization of multi temporal NDVI was
executedusingthefollowingformula:
[(NDVIn*100)+100]
Then, all normalized NDVI images were stacked together. The fortnights of growing
season (JuneOctober) have been taken into account in this study. After stacking, the
fortnightsofgrowingseasonwereintegratedthroughthefollowingequation.
[15/2(NDVIt+2*NDVIt2+2*NDVIt3+…2*NDVItn)]
Here,NDVItindicatesNDVIofeachfortnightofgrowingseason.
Ontheotherhand,meanrainfallofgrowingseasonofeachraingauge stationwastaken
into account from the year 1983 to 2003. The latitude, longitude and mean rainfall of
each rain gauge stations were copied to coordinate calculatort hroughE RDAS Imagine
9.2softwareforinterpolationpurpose.Thenthex,ycoordinates(inputandoutput)were
savedas.datfile.Afterthat, itwasimportedasASCIIfileofpointcoverageto makea
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vectormapofcoordinatesystem.Afterthis, ArcGIS 9.3wasusedtointerpolaterainfall
ofallstations.TheInverseDistanceWeighted (IDW)methodwithpower2wasusedto
makeinterpolationmapofallyears.Sincethismethodassumesthatthingsthatareclose
tooneanotherare more alikethanthosethatarefartherapart.Thenalllayersofrainfall
havebeenstackedandthensubsetofthestudyareawasgenerated.
After preparing thedat abase for the analysis, the correlationco efficients were obtained
from the regression analysis between integrated NDVI and mean rainfall. The analysis
wasdonespatiallyorinpixelbasistoshowthathowfarNDVIofeachpixelisdependent
uponrainfallreceivedbythearea representedbyeachpixel.Itwasperformedbasedon
thelogicthattheNDVIandNetPrimaryProductivityofanareaarestronglydetermined
bytheamountofrainfallreceived.TheNPPvaluesalonemaynotserveasanindicatorof
desertification without taking the rainfall into account (Prince et al., 1998). In arid and
semiarid lands seasonal sums of multitemporal NDVI has found strongly correlated
withvegetationproduction(PrinceandTucker,1986;Prince,1991;NicholsonandFarrar,
1994;Nicholsonetal.,1998;Wesselsetal.,2006).Also,multitemporalNDVIhasbeen
usedbymanyresearchers(Anyamba,Tucker,2005,Herrmannetal.,2005)tofindlong
termvegetation changes.Past researchesdenote that longtermvegetationstress canbe
identifiedbylongtermNDVIdataandthusitcanbeusefulformonitoringdesertification
processes.Forthisreason,atimetrendanalysiswasperformedusingthemultitemporal
integratedNDVItoobservethespatiotemporalpatternofvegetationconditionofChuru
district.ThetemporaltrendofNDVIwascomputedforeachpixelareausinglinearleast
squareregressionover theperiod1983 to2003.Thistechnique representsasimple, yet
robust,wayto reveallongtermtrendsin a temporalsequence ofdatathat departsfrom
the short term annual fluctuations (Hellden, U., Tottrup, C., 2008). The regression and
time trend analysis was performed through in built model maker tool of ERDAS
IMAGINE 9.2 and ENVI 4.7 software. Intersection of time trend map of NDVI and
correlationcoefficient ofrainfallNDVI usedto quantify the areas under theprocess of
desertificationresponsetoclimatechange.
4.ResultsandDiscussion
Severalprevious researches haveproduced a strongpositiverelationshipbetweenNDVI
and rainfall in dry regions all over the world. Although, response of vegetation to
precipitationvariesbetweengeographicalregionsandvegetationtypes(Li,B.etal.,2002,
Li,J.etal.,2004,Nicholsonetal.,1994),mostofthestudiesvotedforprecipitationasa
strongindicatorofvegetation.Thespatialpatternofaverage growingseason NDVI and
rainfallover theperiod19832003hasbeenillustratedinfigure2. Theaveragegrowing
seasonrainfallofpasttwentyoneyear’svariesbetween200500mm.Therainfallmainly
occurs during monsoon and extends from July to September. The spatial pattern of
rainfall shows that it is gradually declining from southeast to northwest. Theaverage
growingseasonNDVIofpasttwentyoneyearshowmoreorlesssimilarspatialpattern.
It has also been decreased from southeast to northwest corresponding with pattern of
rainfallintheregion(figure2).
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Figure2:MeanRainfallandNDVI(19832003)
ThecorrelationbetweenintegratedNDVIandrainfallis illustrated infigure3,revealing
high correlation between the two parameters exists in the Northern part of the district
whereas the South Eastern part surprisingly experiences a reverse condition. These two
distinctcasessaythatthevegetationresponsetorainfallhasbecomemorepronouncedin
the Northern part of the district while there is less impact of rainfall on vegetation
condition of South Eastern region of the district. The areas with significant positive
correlationcoefficientdemarktheclimaticinfluenceonvegetationconditionwhereasthe
areas with negative coefficient indicate intrusion of anthropological factors rather than
climatic factors. The map of correlation coefficient clearly distinguishes two type of
vegetation,oneisinfluencedbyclimateandotherisinfluencedbyhuman.
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Figure3:CorrelationCoefficient(r)betweenintegratedNDVIandRainfall(left);NDVI
TimeTrend(right)
Alteration of vegetation cover can be happened both by climate change and
anthropological activities. To identify the areas under desertification process, the time
trend of growing season NDVI (19832003) was calculated for the district Churu,
illustratedinfigure3(right). The mapdisplays two categoriesofNDVItrends:positive
trendswhichareconsideredto representimprovementof vegetationcoverand negative
trendsindicatingadecliningtrendinvegetationcover.StrongnegativetrendsofNDVIin
some parts of the district suggest degradation of vegetation cover during the past two
decades. On contrary, moderate to high positive trend is also notable over some areas
indicating greening of those areas within last 21 years. Over the entire district, about
52.03% of all pixels experienced a moderate to high declining trends of NDVI while
13.28%ofallpixelsundergoneanincreasingtrendofvegetation(figure4).
About34.69%areaoutofthewholedistricthasastablevegetationcondition(figure4).
The long term degradation of vegetation as monitored by NDVI is an indicator of
desertification (Hill, J., et al, 2008). It is noteworthythat the decreasing or increasing
trend of NDVI as an indicator of desertification is a combined result of climate and
anthropological activities. To detect the areas under climate induced desertification
process, both coefficient mapand time trend map were used. The areasof significant
positivecorrelation between multitemporalNDVI andrainfallwith decreasingtrendof
NDVI,indicatesvegetationdegradationresponsetoclimatechange.Beside this,human
induced desertification is being noticed in the areas of significant negative correlation
betweenmultitemporalNDVIandrainfallwithdecreasingtrendofNDVI.
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Figure4:Areawisedistribution(%)ofNDVItimetrend(left);Measurementofarea(%)
affectedbyclimateinducedandhumaninduceddesertification(right)
Itwasfoundthatabout64.54%ofareaunderdesertificationiscausedbyclimateinduced
processes and 35.46% area is undergone a human induced change of vegetation cover.
Thelongtermclimate induceddegradationofvegetationindicates a slowchangeinthe
patternanddistributionofrainfall.Highevapotranspirationexceedingrainfallalongwith
strong winds is loweringthe soil moisture and making themdry while fine sand grains
blowingfromtheTharDesertslowlyalteringthetextureofsoilanddecliningtheprimary
productivity. Besides this, increasing trend of population pressure also accelerating the
problemofovergrazingandoverploughingwhich madetheareavulnerable.Thestudy
shows,thisarea isgraduallydesertifyingasacomplexconsequenceof bothclimateand
anthropogenicfactors.
5.Conclusions
The results obtained from the study reveals that the NOAA AVHRR data can
successfully monitor and identify areas under the several process of desertification
response to climate change. The correlation betweenNDVI and rainfall is prominent in
some areas of Churu which indicates the strong climatic influence on vegetation
conditionofthoseareas.Bothoftheindicatorscanbeusedinremotesensinginformation
based model for evaluating desertification monitoring and estimation. The NDVI time
trend clearly recognizes the areas with long term vegetation degradation indicating the
ongoing desertification process. The study reveals that more than half of the district is
undergone a declining trend of vegetation cover indicating the ongoing process of
desertification. Within this, about 64.54% area is experiencing desertification due to
climatic processes and 35.46% area is undergone human induced desertification
processes.Also,thisremotesensingbasedtechniquehasbecomehelpfultoidentifyareas
undertheprocessofgreening as animpactofanthropogeniceffect. Thedecliningtrend
in vegetation explicitly supports the information on encroachment of the Thar Desert.
Thestudyrevealsthattheglobalavailabilityofcoarsescale,multitemporaldataarchives
ofNOAAAVHRR have greatpotentialto answerthequestions arrivedfromlongterm
vegetationchanges.
Acknowledgement
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TheauthorsexpresstheirsinceregratitudeandutmostrespecttoDr.N.R.Patel,Scientist,
Agriculture and Soils Division, Indian Institute of Remote Sensing, Dept. of Space,
Indian Space Research Organisation, Dehradun, Uttarakhand, India for his expert
directionandsupport.
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