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Monitoring desertification Risk through Climate Change and Human Interference Using Remote Sensing and GIS Techniques

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The threat of global climate change has radically increased the attention directed towards 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 accelerated the conversion of fertile lands into arid lands and this eventually leads to land degradation and desertification. The term “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 Rajasthan are very clearly detected from long term satellite data and it has been used for monitoring desertification process. In this paper, long term NOAAAVHRR (19832003) data has been used to monitor desertification processes through NDVI timetrend. The study is based on the analysis of regional long term changes of vegetation conditions that indicates the ongoing desertification processes. Vegetation growth is entirely depended upon rainfall. Here, long term NDVI trend has been analysed corresponding with the long term annual rainfall (19832003). It identifies the areas affected by desertification process as a circumstance of climate change. The results confirmed that some parts of Churu district is under climatically induced desertification processes.
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INTERNATIONALJOURNALOF GEOMATICSANDGEOSCIENCES
Volume2,No 1,2011
©Copyright2010AllrightsreservedIntegratedPublishingservices
Researcharticle ISSN0976 –4380
SubmittedonJuly2011publishedonSeptember201121
Monitoringdesertificationrisk throughclimatechangeandhuman
interferenceusingRemotesensingandGIStechniques
ArnabKundu
1
,DipanwitaDutta
2
1CentrefortheStudyofRegionalDevelopment,SchoolofSocialSciences,Jawaharlal
NehruUniversity,NewDelhi110067,India.
2IndianInstituteofRemoteSensing,DepartmentofSpace,IndianSpaceResearch
Organisation,Dehradun248001,Uttarakhand,India.
arnknd@live.in
ABSTRACT
Thethreatofglobalclimatechangehasradicallyincreasedtheattentiondirectedtowards
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
acceleratedtheconversionoffertilelandsintoaridlandsandthiseventuallyleadstoland
degradation and desertification. Theterm “desertification” indicates land degradation in
arid, semiarid and dry subhumid 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
Rajasthanareveryclearlydetectedfromlongtermsatellitedataandithasbeenusedfor
monitoringdesertificationprocess.Inthispaper,longtermNOAAAVHRR(19832003)
data has been used to monitor desertification processes through NDVI timetrend. The
studyisbasedontheanalysisofregionallongtermchangesofvegetationconditionsthat
indicates the ongoing desertification processes. Vegetation growth is entirely depended
uponrainfall.Here,longtermNDVItrendhasbeenanalysedcorrespondingwiththelong
termannualrainfall(19832003).Itidentifiestheareasaffectedbydesertificationprocess
as a circumstance of climate change. The results confirmed that some parts of Churu
districtisunderclimaticallyinduceddesertificationprocesses.
Keywords: Climate change, Land Degradation, Desertification, Vegetation cover,
NOAAAVHRRNDVI,Rainfall.
1.Introduction
According to Adger et al., (2000) over 250 million people are directly affected by
desertificationandsomeonebillionpeopleinover100countriesareatrisk.India,being
oneofthe leadingdevelopingcountriesof theworld is notexemptedfromtheproblem
related to various natural hazards. Among them,desertification hase merged as a major
economic,socialandenvironmentalprobleminwestern partofIndia.The"GreatIndian
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
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
22
Rajasthanwhichcoverabout61%ofthegeographicalareaoftheRajasthan(Sinhaetal.,
2000). Encroachment of the Thar Desert towards its Eastern boarder has become a
seriousproblemtothe adjoiningdistrictsofthedesert. Itisslowlycapturingthe 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 in197778 with the objectives to control desertification, restore
the ecological balance of desert and semidesert areas and create conditions for raising
thelevelofproduction,incomeandemploymentofthepopulationoftheseareas.Inspite
ofseveralattemptstakenbyour Government,thereislackofwellplannedmanagement
and actual information on climate and human induced desertification. It is true that
climateinduceddesertificationisinevitableanddifficulttoprevent.But,itispossibleto
identify the areas exposed to desertification processes and that would be useful for
makingastrategytopreventtheexpansionofthedesert.Differentmethodsofevaluating
desertification include the use of direct observation and measurement, mathematical
models and parametric equation, estimates, remote sensing and indicators (Rubio and
Bochet, 1998). Nowa 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.TheimportanceofindicatorsinmonitoringdesertificationwasrecognizedbyFAO
and UNEP in the year of 1980 and they proposed 22 indicators in the Provisional
Methodologyfor Assessment andMappingofDesertification.LipingDi,(2003) madea
detailedstudyonrecentprogressofremotesensingonmonitoringofdesertificationand
mentioned that remote sensing is the only tool of choice for desertification studies at
regionalandglobalscale.Remotesensinghasbeensuccessfullyappliedtotheprocessof
monitoring desert expansion and to the assessment of factors that cause desertification
(Hananetal.,1991).Thereisadistincteffectofdesertificationonvegetationcover.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
AVHRRdataisanestablishedtechniquefor monitoringlongtermchangesinvegetation
cover.TheNDVIanditsrelationtogreenbiomasswasfirstsuggestedanddemonstrated
byRouseet al., (1973)andTucker(1979).It is one ofthemost widelyused vegetation
indexanditsutilityinsatelliteassessmentandmonitoringofglobalvegetationcoverhas
been well exploited over the past two decades (Huete and Liu, 1994; Leprieur et al.,
2000).Inhisstudy,Zhang(1999)founda strongcorrelation(R
2
=0.73)betweenNOAA
AVHRRNDVIandVegetationcover.Thepresentstudyattemptstoinvestigatetheareas
experiencinglongtermdegradationofvegetationcoverresponsetoclimatechangeinthe
district, Churu. Here, two indicators of desertification have been selected to identify
climateinduceddesertification,oneislongtermrainfallandtheotherisremotesensing
basedindicatorNDVI.
2.Studyarea
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,
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
23
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
populationof19,22,908personswithadensityof123peoplepersquarekm.Thedistrict
encompasses large shifting sand dunes andhas a varying altitude of213 to 400 meters
aboveMeanSeaLevel.
Figure1:StudyArea
Note:DungargarhtehsilisnowadjoinedwithBikanerdistrictofRajasthan
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).Climaticallytheregionbelongstohyperaridtypeofclimatewithhighdiurnaland
annual range of temperature, scanty rainfall, dry scorching winds and low relative
humidityresultinghigherrateofevaporation.Thiskindofclimatefuelsingeneratingand
transportingofloosesandordustparticles.Theregionrecordstemperaturerangingfrom
below freezing point in the winters to over 50 degrees in the summer afternoons. The
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
24
pattern of rainfall varies spatially; it increases from West to East. The district is
characterizedbysandyto sandyloamcalcareous typeofsoilwhichiscoarse intexture,
lessstructuredwithnegligibleamountoforganicmatter.Asaresultofit,thesubsurface
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
poorvegetationcover,theareatowardseastisgreenerthanwest.Largeareasarecovered
with thorny scrubs, grasses with isolated trees. The scarcity of vegetation covers is
strengtheningtheAeolianprocessesandmakingthesanddunesmobile.Theeconomyof
Churuismainlybasedonagricultureandanimalhusbandry.Themajorcropsareoilseeds,
Wheat,Jowar(Sorghum),kharifpulsesandbajra(pearlmillet).
3. MaterialsandMethod
3.1NDVIData
TheNDVIisagoodindicatorofgreenbiomass,leafareaindexandpatternofproduction
(Thinkableetal.2004).Thefundamentalbehindthisindexisthattheinternalmesophyll
structureofhealthygreenleavesstronglyreflectsNIRradiationandleafchlorophylland
otherpigmentsabsorba largeproportionoftheredVISradiation.Thisbecomesreverse
incase ofunhealthyor waterstressed vegetation.NDVI iscalculated bythedifference
betweenreflectanceinnearinfrared(NIR)andvisiblered(VIS)bandofelectromagnetic
spectrum.
NDVI=(NIR−VIS)/(NIR+VIS)
The NDVI value variesbetwee n1.0 to +1.0. Itranges from 0.1 in deserts upto 0.8 in
densetropicalrainforest.TheValuesbetween0and0.1denotesrocksandbaresoiland
less than 1 indicate iceclouds, waterclouds, and snow. The NDVI has been used for
descriptionofcontinentallandcover, vegetationclassificationandvegetationphenology
(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;
Tuckeretal.,1991;Nicholsonetal.,1998;Princeetal.,1998;DioufandLambin,2001;
Anyamba and Tucker, 2005; Olsson et al., 2005). NDVI is calculated from channel
1(visible) andc hannel 2(infrared) of AVHRR. In thisst udy, fortnightly GIMMS NDVI
fromNOAA(AVHRR)hasbeenusedforatimeperiodof21years(1983– 2003).This
datawascollectedfromtheNationalOceanicand AtmosphericAdministration(NOAA)
satellitewhichholdsthe AdvancedVeryHighResolutionRadiometer (AVHRR)sensor
andprimarilyoperatedbyUSA.Thesesensorscollecttheglobaldataonadailybasisfor
amultiplicityof land,ocean,andatmosphericapplications.Besidesthese,itisalsoused
to monitor forest fire, analysis of vegetation, weather forecasting, climatic condition,
study of drought, measurement of global sea surface temperature and ocean related
research.TheNDVIisconsideredasa‘greenness’indexinstudiesofdrylandvegetation
cover. It has found that in arid and semiarid regions, NDVI is well correlated with
parameterssuchas leafareaindex,Greenleaf,biomass,vegetationcover,etc.(Nicholson
et al., 1998). In his study, Zhang (1999) also found a strong correlation (R
2
=0.73)
betweenNOAAAVHRRNDVIandVegetationcover.
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
25
Table1: CharacteristicsofNOAAAVHRRsensor
Characteristics NOAAAVHRR
InclinationofOrbit 98.922º
Heightabovesurface 851Km
Numberoforbits/day 14.1
Timesofcoverageatequator
01:41Descending
13:41Ascending
OrbitalPeriod 102min
LatitudinalCoverage 90ºN90ºS
CycleDuration 1Day
GroundCoverage 2842Km
FieldofView(FOV) ±55.4º
InstantaneousFieldofView(IFOV 1.391.51mrad
GroundResolution(Nadir) 1.1Km
NumberofChannels
OneVisible(0.50.7um)
OneNearInfrared(0.71.1um)
OneMiddleInfrared
TwoThermalInfrared
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 theG lobal InventoryModelling andMo nitoring System
(GIMMS)groupatNASA’sGoddard Space FlightCentre.Forthisresearch,fortnightly
NDVI data was gathered from already processed 15day NDVI composites using the
maximum value compositing procedure to minimize effects of cloud contamination,
varyingsolar zenithanglesand surface topography(Holben, 1986).The Preprocessing
of 15 day composite GIMMSNDVI (1983 – 2003) data was carried out through
followingsteps:
1. ConversionfromGEOtiffformatto.imgformat
2. LayerStacking
3. Reprojection
4. Scaling
5. Subset
TheGIMMS NDVI dataisavailableinGEOtiffformatwhichwerefirstconvertedinto
image format. Then this 15 day composite dataset of 21 years (19832003) has been
stacked. Each stacked layer of all years encloses ten layersrepresenting ten fortnights
(JuneOctober) of growing season. These stacked layers were then reprojected into
AlbersEqualArea ProjectionwithWGS84 datum.Thisprojectionwas chosento keep
the similar pixel size. The following projection parameters are given for Albers Equal
Area Projection for India. Theser eprojected images wererescaled to retain theNDVI
valuerangingfrom+1to1usingthescalefactor0.001.
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
26
ParametersusedforAlbersEqualAreaProjection:
1. SpheroidName:WGS84
2. DatumName:WGS84
3. Latitudeof1stStandardParallel:12ºN
4. Latitudeof2ndStandardParallel:28ºN
5. LongitudeofCentralMeridian:78ºE
6. Latitudeoforiginofprojection:20ºN
7. FalseEastingatcentralmeridian:2000000.0mts.
8. FalseNorthingatorigin:2000000.0mts.
3.2RainfallData
Longterm (19832003) monthly Rainfall data from India Meteorological Department
(IMD) were usedin this study. Monthly rainfall data of growing season( JuneOctober)
were collected from different rain gauge stations scattered in and around of the Churu
district. The rainfall of different months of growingseaso n was thena veraged for each
raingaugestationtoobtainthemeanrainfallofgrowingseason.
3.3Methodology
Thestudywascarriedout aimingto agoaltoidentifyareasundergoingclimateinduced
desertificationprocessesthroughremotesensingbasedindicatorNDVIandclimatebased
indicator rainfall. The data was processed to make it ready for further geostatistical
analysis. After preprocessing of the AVHRRNDVI images (19832003), they were
normalized for regression analysis. The normalization of multi temporal NDVI was
executedusingthefollowingformula:
[(NDVIn*100)+100]
Then, all normalized NDVI images were stacked together. The fortnights of growing
season (JuneOctober) have been taken into account in this study. After stacking, the
fortnightsofgrowingseasonwereintegratedthroughthefollowingequation.
[15/2(NDVIt+2*NDVIt2+2*NDVIt3+…2*NDVItn)]
Here,NDVItindicatesNDVIofeachfortnightofgrowingseason.
Ontheotherhand,meanrainfallofgrowingseasonofeachraingauge stationwastaken
into account from the year 1983 to 2003. The latitude, longitude and mean rainfall of
each rain gauge stations were copied to coordinate calculatort hroughE RDAS Imagine
9.2softwareforinterpolationpurpose.Thenthex,ycoordinates(inputandoutput)were
savedas.datfile.Afterthat, itwasimportedasASCIIfileofpointcoverageto makea
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
27
vectormapofcoordinatesystem.Afterthis, ArcGIS 9.3wasusedtointerpolaterainfall
ofallstations.TheInverseDistanceWeighted (IDW)methodwithpower2wasusedto
makeinterpolationmapofallyears.Sincethismethodassumesthatthingsthatareclose
tooneanotherare more alikethanthosethatarefartherapart.Thenalllayersofrainfall
havebeenstackedandthensubsetofthestudyareawasgenerated.
After preparing thedat abase for the analysis, the correlationco efficients were obtained
from the regression analysis between integrated NDVI and mean rainfall. The analysis
wasdonespatiallyorinpixelbasistoshowthathowfarNDVIofeachpixelisdependent
uponrainfallreceivedbythearea representedbyeachpixel.Itwasperformedbasedon
thelogicthattheNDVIandNetPrimaryProductivityofanareaarestronglydetermined
bytheamountofrainfallreceived.TheNPPvaluesalonemaynotserveasanindicatorof
desertification without taking the rainfall into account (Prince et al., 1998). In arid and
semiarid lands seasonal sums of multitemporal NDVI has found strongly correlated
withvegetationproduction(PrinceandTucker,1986;Prince,1991;NicholsonandFarrar,
1994;Nicholsonetal.,1998;Wesselsetal.,2006).Also,multitemporalNDVIhasbeen
usedbymanyresearchers(Anyamba,Tucker,2005,Herrmannetal.,2005)tofindlong
termvegetation changes.Past researchesdenote that longtermvegetationstress canbe
identifiedbylongtermNDVIdataandthusitcanbeusefulformonitoringdesertification
processes.Forthisreason,atimetrendanalysiswasperformedusingthemultitemporal
integratedNDVItoobservethespatiotemporalpatternofvegetationconditionofChuru
district.ThetemporaltrendofNDVIwascomputedforeachpixelareausinglinearleast
squareregressionover theperiod1983 to2003.Thistechnique representsasimple, yet
robust,wayto reveallongtermtrendsin a temporalsequence ofdatathat departsfrom
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
correlationcoefficient ofrainfallNDVI usedto quantify the areas under theprocess of
desertificationresponsetoclimatechange.
4.ResultsandDiscussion
Severalprevious researches haveproduced a strongpositiverelationshipbetweenNDVI
and rainfall in dry regions all over the world. Although, response of vegetation to
precipitationvariesbetweengeographicalregionsandvegetationtypes(Li,B.etal.,2002,
Li,J.etal.,2004,Nicholsonetal.,1994),mostofthestudiesvotedforprecipitationasa
strongindicatorofvegetation.Thespatialpatternofaverage growingseason NDVI and
rainfallover theperiod19832003hasbeenillustratedinfigure2. Theaveragegrowing
seasonrainfallofpasttwentyoneyear’svariesbetween200500mm.Therainfallmainly
occurs during monsoon and extends from July to September. The spatial pattern of
rainfall shows that it is gradually declining from southeast to northwest. Theaverage
growingseasonNDVIofpasttwentyoneyearshowmoreorlesssimilarspatialpattern.
It has also been decreased from southeast to northwest corresponding with pattern of
rainfallintheregion(figure2).
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
28
Figure2:MeanRainfallandNDVI(19832003)
ThecorrelationbetweenintegratedNDVIandrainfallis illustrated infigure3,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
distinctcasessaythatthevegetationresponsetorainfallhasbecomemorepronouncedin
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
correlationcoefficientdemarktheclimaticinfluenceonvegetationconditionwhereasthe
areas with negative coefficient indicate intrusion of anthropological factors rather than
climatic factors. The map of correlation coefficient clearly distinguishes two type of
vegetation,oneisinfluencedbyclimateandotherisinfluencedbyhuman.
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
29
Figure3:CorrelationCoefficient(r)betweenintegratedNDVIandRainfall(left);NDVI
TimeTrend(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 (19832003) was calculated for the district Churu,
illustratedinfigure3(right). The mapdisplays two categoriesofNDVItrends:positive
trendswhichareconsideredto representimprovementof vegetationcoverand negative
trendsindicatingadecliningtrendinvegetationcover.StrongnegativetrendsofNDVIin
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%ofallpixelsundergoneanincreasingtrendofvegetation(figure4).
About34.69%areaoutofthewholedistricthasastablevegetationcondition(figure4).
The long term degradation of vegetation as monitored by NDVI is an indicator of
desertification (Hill, J., et al, 2008). It is noteworthythat 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 mapand time trend map were used. The areasof significant
positivecorrelation between multitemporalNDVI andrainfallwith decreasingtrendof
NDVI,indicatesvegetationdegradationresponsetoclimatechange.Beside this,human
induced desertification is being noticed in the areas of significant negative correlation
betweenmultitemporalNDVIandrainfallwithdecreasingtrendofNDVI.
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
30
Figure4:Areawisedistribution(%)ofNDVItimetrend(left);Measurementofarea(%)
affectedbyclimateinducedandhumaninduceddesertification(right)
Itwasfoundthatabout64.54%ofareaunderdesertificationiscausedbyclimateinduced
processes and 35.46% area is undergone a human induced change of vegetation cover.
Thelongtermclimate induceddegradationofvegetationindicates a slowchangeinthe
patternanddistributionofrainfall.Highevapotranspirationexceedingrainfallalongwith
strong winds is loweringthe soil moisture and making themdry while fine sand grains
blowingfromtheTharDesertslowlyalteringthetextureofsoilanddecliningtheprimary
productivity. Besides this, increasing trend of population pressure also accelerating the
problemofovergrazingandoverploughingwhich madetheareavulnerable.Thestudy
shows,thisarea isgraduallydesertifyingasacomplexconsequenceof bothclimateand
anthropogenicfactors.
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 betweenNDVI and rainfall is prominent in
some areas of Churu which indicates the strong climatic influence on vegetation
conditionofthoseareas.Bothoftheindicatorscanbeusedinremotesensinginformation
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,thisremotesensingbasedtechniquehasbecomehelpfultoidentifyareas
undertheprocessofgreening as animpactofanthropogeniceffect. Thedecliningtrend
in vegetation explicitly supports the information on encroachment of the Thar Desert.
Thestudyrevealsthattheglobalavailabilityofcoarsescale,multitemporaldataarchives
ofNOAAAVHRR have greatpotentialto answerthequestions arrivedfromlongterm
vegetationchanges.
Acknowledgement
MonitoringdesertificationriskthroughclimatechangeandhumaninterferenceusingRemotesensing
andGIStechniques
ArnabKundu,DipanwitaDutta
InternationalJournalofGeomaticsandGeosciences
Volume2Issue1,2011
31
TheauthorsexpresstheirsinceregratitudeandutmostrespecttoDr.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
directionandsupport.
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... An increasing amount of data indicates that using the Red-Edge spectral band can improve the sensitivity and accuracy of plant study, especially in areas with little flora, including semi-arid and dry regions (Jha 2010 ;Kundu & Dutta, 2011;Yanli et al., 2012). It is essential to detect decreases in proportion to the initial level in order to evaluate the severity of drought and estimate the process of desertification (Weier & Herring, 2012). ...
... This correction factor is applied to minimize the influence of background sensitivity in the study, as highlighted by Chen in 1995. In their work, Kundu and Dutta (2011) utilized NDVI time trend and long-term rainfall data to illustrate the gradual process of desertification in the Rajasthan region. This event was attributed to a complex interplay between anthropogenic and climatic factors (Shafie et al. 2012). ...
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... Nowadays, RS is used to track the desertification process by identifying suitable indicators as proposed by FAO and UNEP. Due to its encroachment on the eastern boundary, the Great Indian Desert, also known as the Thar Desert, has become a challenge for the surrounding regions [12]. Advanced methods like global positioning systems (GPS), geographic information systems (GIS), and remote sensing (RS) can be particularly useful in evaluating and controlling them. ...
... The mean rainfall for the growing season was calculated by averaging the rainfall of different months throughout the growing season for each rain gauge station. The correlation coefficients between integrated NDVI and mean rainfall were derived from the regression analysis after preparing the database for the analysis [12]. ...
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Regional variances in climate, soil, and topography make agricultural production systems particularly fragile. Animal health are negatively impacted by variations in air temperature, precipitation, frequency, and intensity of extreme weather events. For its assessment and administration, cutting-edge methods like remote sensing (RS), global positioning systems, and geographic information systems (GIS) might be very beneficial. The RM & GIS are essential tools with numerous applications for tackling these problems. The impact of climatic and human-induced changes on the environment is receiving more attention as a result of climate change. Due to climate change and human activity, "desertification" describes the degradation of land in arid, semiarid, and dry sub-humid regions. Natural resource sustainability in changing climates can be obtained with the application of RS and GIS. In this review article, the issues towards wildlife were demonstrated and the application of remote sensing was discussed to reduce the impact of climate change to save the wildlife and its preservation. Further, the bibliometric analysis was conducted via R-studio Bibliometric tool, which entailed that developed countries (USA, Canada, Germany) are more forward to applying remote sensing tool to mitigate climate risks. Received: 18 June 2023 | Revised: 25 July 2023 | Accepted: 16 September 2023 Conflicts of Interest The author declares that she has no conflicts of interest to this work. Data Availability Statement Data available on request from the corresponding author upon reasonable request.
... 0.43, and 0.34, respectively, over Gautam Budha Nagar, India (Sharma et al., 2022). The long-term variation of precipitation and temperature and its effect on the annual crop production has been observed using Landsat data over India (Basistha et al., 2009;Kundu and Dutta 2011;Duhan and Pandey, 2013;Gautam et al., 2020;Dutta et al., 2015;Sahoo et al., 2015;Kundu et al., 2017). The precipitation value at each station has been interpolated using ArcGIS 9.3 to find the spatial variation of rainfall. ...
... Duhan et al. (2013) showed that mean annual precipitation has varied from 694 mm (at Westnimar) to 1416 mm (at Mandla). Kundu and Dutta (2011) demonstrated a varying pattern of vegetation dynamics in response to rainfall over the Bundelkhand area. Sahoo et al. (2015) found a good agreement between satellite-derived and meteorological drought indices. ...
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The paper investigates the long-term spatiotemporal characteristics of various satellite-derived vegetation indices (VI), such as the Normalized Difference Vegetation Index (NDVI) and Enhanced Vegetation Index (EVI), as well as Gross Primary Productivity (GPP) and Sun-induced Chlorophyll Fluorescence (SIF) over the Kolkata conurbation and its surrounding areas from 2003 to 2016. Additionally, it analyzes the correlation between these vegetation indices and atmospheric parameters like rainfall, soil moisture (SM), evapotranspiration (ET), and land surface temperature (LST). Monthly variations of these parameters are observed, and inter-annual variability is examined using linear regression techniques. The study also observes the time average spatial correlation between vegetation indices and weather parameters. Moreover, it investigates the time-lag effect (0, 1, 2, and 3 months) using Pearson correlation coefficient analysis between VI and other meteorological parameters. NDVI and EVI exhibit maximum correlation with rainfall, SM, ET, and LST within specific lag periods. NDVI and EVI show a slow response rate to rainfall, and their sensitivity depends on SM and ET. A positive correlation is observed between NDVI and ET, indicating that NDVI increases with vaporized water in the atmosphere. A negative correlation is noted between NDVI and LST in the region studied. The study’s insights are valuable for predicting future vegetation index characteristics based on meteorological parameters in tropical urban areas like Kolkata and its surroundings. This predictive capability can aid in mitigating adverse weather effects on vegetation.
... Furthermore, per capita water resources of Zhengzhou amount to only half of the provincial average, coupled with an uneven distribution of precipitation, rendering its water system intrinsically fragile. Consequently, the stronger negative effects resulting from human activities exacerbate the developmental disparities between the two systems [55]. Figure 6 shows the spatial distribution of HDI and WDI in Henan Province from 2007 to 2022. ...
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There is an interdependent symbiotic relationship between humans and water; scientific and effective assessment of the human–water symbiosis relationship is of great significance for the promotion of sustainable development. This study developed a novel framework of the human–water symbiosis relationship under an integrated perspective, which included theoretical interpretation, quantitative assessment, pattern discrimination, and an attribution analysis. Based on the symbiosis theory, the theoretical analysis of the human–water relationship was carried out to analyze the three basic elements of the human–water system, and then the evaluation index system of the human–water symbiosis system was constructed to quantitatively assess the development level of the human system and the water system. The Lotka–Volterra model was used to identify the symbiotic pattern, and the human–water symbiosis index was calculated to characterize the health state of the human–water symbiosis system. The main influencing factors of the human–water symbiosis system were further identified through an attribution analysis. Finally, a case study was carried out with 18 cities in Henan Province. Results reveal that (a) the proposed method can effectively realize the quantitative characterization of the human–water symbiosis relationship, with good applicability and obvious advantages; (b) the human–water symbiosis pattern of cities in Henan Province is dominated by the “human system parasitizes water system (H+W−)” pattern, and more attention should be paid to the water system in the subsequent development of it; and (c) the main factors influencing the human system, the water system, and the human–water symbiosis system are the research and development (R&D) personnel equivalent full-time (H7), per capita water resources (W1), and proportion of water conservancy and ecological water conservancy construction investment (W6), respectively. The findings can provide theoretical and methodological support for the study of the human–water symbiosis relationship and sustainable development in other regions.
... Therefore, we argue that in addition to controlling GHG emissions, more local efforts need to be devoted to countering desertification in West and South Asia to reduce potential natural dust emissions. In arid and semi-arid regions, continued desertification due to human activities could worsen airborne dust level, even when weather conditions are not conducive for dust emission (79,80). Although natural sources contribute more significantly to total dust loading, rapid urbanization, and industrialization, along with increased construction activities, road dust, and vehicular emissions, also contributed to high levels of anthropogenic dust emissions in West and South Asia in recent decades (81,82). ...
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Dust loading in West and South Asia has been a major environmental issue due to its negative effects on air quality, food security, energy supply and public health, as well as on regional and global weather and climate. Yet a robust understanding of its recent changes and future projection remains unclear. On the basis of several high-quality remote sensing products, we detect a consistently decreasing trend of dust loading in West and South Asia over the last two decades. In contrast to previous studies emphasizing the role of local land use changes, here, we attribute the regional dust decline to the continuous intensification of Arctic amplification driven by anthropogenic global warming. Arctic amplification results in anomalous mid-latitude atmospheric circulation, particularly a deepened trough stretching from West Siberia to Northeast India, which inhibits both dust emissions and their downstream transports. Large ensemble climate model simulations further support the dominant role of greenhouse gases induced Arctic amplification in modulating dust loading over West and South Asia. Future projections under different emission scenarios imply potential adverse effects of carbon neutrality in leading to higher regional dust loading and thus highlight the importance of stronger anti-desertification counter-actions such as reforestation and irrigation management.
... As reported by Sinha et al. [9], Rajasthan alone harbors 91% of India's desert, covering an extensive 2.08 million square kilometers, which constitutes approximately 61% of the state's total geographical area. According to Kundu and Dutta [10], the western areas of the state are classified as part of the vast Great Indian Desert. However, desertification issues also pose a threat to districts such as Bikaner, Churu, and Nagaur. ...
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A study of the extended desertification due to anthropogenic causes under climate change (CC) associated with its impact is presented here. Desertification, the main environmental issue, severely impacts agricultural output, causing poverty and economic instability in a nation like India. The regional distribution of desertification was determined using the RF and MaxEnt models. The western, central, and southern portions of the nation are very high, high, and moderately susceptible to desertification, respectively, according to the RF model. The MaxEnt model indicates that the western, central, and southern parts of the country exhibit a significant susceptibility to desertification, with the eastern parts also showing a moderate level of vulnerability. The remaining portion of this region, mainly in the north, east, and northeast, is particularly resistant to desertification. The outcome demonstrated that the country's desertification process had expanded from the west to the south. However, there are some spatial differences associated with the mentioned part of the country. This relevant information is crucial for decision maker of this country to take suitable remedies in regard to the reduction of the intensity of desertification.
... Therefore, the frequent occurrence of drought conditions in the arid and semi-arid regions is attributed to low rainfall and high variability. These findings concur with those of Saini et al. [33], Narain et al. [50], and Kundu and Datta [51]. ...
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Understanding the dynamics of vegetative greenness and how it interacts with various hydroclimatic factors is crucial for comprehending the implications of global climate change. The present study utilized the MODIS-derived normalized difference vegetation index (NDVI) to understand the vegetation patterns over 21 years (2001–2021) in Rajasthan, India. The rainfall, land surface temperature (LST), and evapotranspiration (ET) were also analyzed. The changes, at a 30 m pixel resolution, were evaluated using Mann–Kendall’s trend test. The results reveal that the NDVI, ET, and rainfall had increasing trends, whereas the LST had a decreasing trend in Rajasthan. The NDVI increased for 96.5% of the total pixels, while it decreased for 3.4% of the pixels, of theh indicates vegetation improvement rather than degradation. The findings of this study provide direct proof of a significant reduction in degraded lands throughout Rajasthan, particularly in the vicinity of the Indira Gandhi Canal command area. Concurrently, there has been a noticeable expansion in the cultivated land area. The trend of vegetation decline, particularly in the metro cities, has occurred as a result of urbanization and industrialization. In contrast to the LST, which has a decreasing gradient from the western to eastern portions, the spatial variability in the NDVI, ET, and rainfall have decreasing gradients from the southern and eastern to western regions. The results of correlations between the vegetative indices and hydroclimatic variables indicate that the NDVI has a strong positive correlation with ET (r2 = 0.86), and a negative correlation with LST (r2 = −0.55). This research provides scientific insights into vegetation change across Rajasthan, and may help the state to monitor vegetation changes, conserve ecosystems, and implement sustainable ecosystem management.
... There are more than 100 countries that are at risk of desertification, striking some of the most vulnerable and poorest populations the hardest, as subsistence farming is widespread in many of the impacted areas (Adger et al., 2000). There are more than one billion people who are in potential danger due to this environmental crisis, and this problem affects about 250 million people (Kundu & Dutta, 2011). In a decertified zone, which encompasses a total area of between 6 and 12 million square kilometres worldwide, between 1 and 6% of the population resides (Xu et al., 2019). ...
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The purpose of this study is to evaluate the desertification vulnerability and the future trends of desertification expansion in the Bahawalpur division of Punjab, Pakistan. This aim is achieved by analyzing Landsat data between the years 1990 and 2019. The biophysical index and socio-economic index were used to identify the Desertification Vulnerability Index (DVI) and its changes which have taken place over the study period between the years 1990 and 2019. The findings indicated that there was a decrease in the rate of desertification vulnerability from 1990 to 2019. In addition, the central and southern part of the Bahawalpur division is classified as a highly vulnerable zone in comparison to the other part of the region. The overall results show that the barren land and the desert area have been showing a decreasing trend, accompanied by substantial growth in vegetation from 1990 to 2019. The findings of the DVI analysis indicate that the Highly Vulnerable Area has decreased spatially from 61.12 in 1990 to 55.3% in 2019, while the Moderately Vulnerable Area and the Least Vulnerable Area have grown from 25.59% and 17.2% in 1990 to 28.56 and 19.53% in 2019, respectively. The decreasing trend demonstrates the effectiveness of efforts to combat desertification and the government could develop the best strategies for rehabilitation works and control the land degradation process in the most vulnerable areas in the Bahawalpur division of Punjab, Pakistan.
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The objective of this research is to assess the effects of climate change on Türkiye by utilizing data catalogues provided by the Google Earth Engine (GEE) cloud-computing platform. The utilized data catalogues encompassed precipitation, Land Surface Temperature (LST), EvapoTranspiration (ET), Potential EvapoTranspiration (PET), Normalized Difference Vegetation Index (NDVI), Enhanced Vegetation Index (EVI), Vegetation Condition Index (VCI), and Forest Area Loss (FAL). Data spanning the years 2001-2022 were collected, and analyses were conducted separately for seven geographical regions of Türkiye on both an annual and seasonal basis. Initially, trend analysis techniques were applied to the individual data sets, followed by an examination of correlations among them. Notably, significant decreasing and increasing trends were observed in annual precipitation and LST data in the Eastern Anatolia region, respectively. Furthermore, a significant increasing trend was identified in annual ET data across all regions except Eastern Anatolia. Conversely, significant increasing trends were noted in annual PET data in Eastern Anatolia and the Aegean regions. Additionally, significant increasing trends were discerned in annual NDVI, EVI, and VCI data across all regions. Experiments revealed that the ET exhibited robust correlations with the NDVI (0.77), EVI (0.79) and VCI (0.81). Furthermore, the NDVI demonstrated strong correlations with EVI (0.99) and VCI (0.96).
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Many assumptions have been made about the nature and character of desertification in West Africa. This paper examines the history of this issue, reviews the current state of our knowledge concerning the meteorological aspects of desertification, and presents the results of a select group of analyses related to this question. The common notion of desertification is of an advancing "desert," a generally irreversible anthropogenic process. This process has been linked to increased surface albedo, increased dust generation, and reduced productivity of the land. This study demonstrates that there has been no progressive change of either the Saharan boundary or vegetation cover in the Sahel during the last 16 years, nor has there been a systematic reduction of "productivity" as assessed by the water-use efficiency of the vegetation cover. While it also showed little change in surface albedo during the years analyzed, this study suggests that a change in albedo of up to 0.10% since the 1950s is conceivable.
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India has about 2.34 million km 2 of hot desert called 'Thar' in the western part, mostly covering the state of Rajasthan. After independence strenuous efforts were made towards desertification control, ecological regeneration and restoration of the Thar desert in order to reclaim the productivity of the vast unproductive desert land. For this purpose a 649 km long man made canal was made to bring Himalayan water into the water starved desert. Although Thar desert is 'highly generic' i.e. it be-comes lush green with slightest precipitation, its natural rates of regeneration have been very slow due to intense biotic pressure (overgrazing, extraction of fodder and fuelwood). Introduction of fast growing exotic species of trees and grasses from isoclimatic regions of the world for stabilization of shifting sand dunes; creation of 'microclimates' through shelterbelt planta-tions; and creation of 'fencing and enclosures' for regeneration of indigenous species have proved highly successful towards the control of desertification, ecological regeneration and restoration of the Thar desert. The degraded Thar desert ecosystem shows tremendous resilience for regeneration when the influence of biotic factors is removed. The native people of the Thar desert have a grand tradition of preserving village grazing lands called 'gochars', and green woodlands called 'Orans'. Orans are preserved in the name of local diety. The villagers take a vow not to cut down any tree or branches of trees from the Orans. Only the grasses and palatable herbs can be used as fodder for the cattle. Orans and gochars are like 'mini-biosphere reserves' in the Thar desert and have greatly helped in the maintenance of ecological stabil-ity of the region. Thar desert holds a big potential for development into a rangeland. The highly nutritive fodder grasses Lasiurus sindicus, Cenchrus ciliaris, C. setigerus and Cymbopogon jwarancusa are well adapted to the Thar desert environment. INTRODUCTION In India there are about 2.34 million km 2 of hot desert called 'Thar'. It represents one of the most inhospitable arid zones of the world, spreading mostly through western Rajasthan, Gujarat, South-Western Punjab, Haryana and part of Karnataka. About 85% of the great Indian desert lies in India and the rest in Pakistan. About 91% of the desert, i.e. 2.08 million km 2 , falls in Rajasthan covering about 61% of the geographi-cal area of the state. The Aravali hills, older than the Himalayas, intersect the State to the north-east and in the west lies the great Indian desert the 'Thar'. The Indian desert is characterized by high velocity wind, huge shifting and rolling sand dunes; high diurnal variation of temperature; scarce rainfall; intense solar radia-tion and high rate of evaporation. Thar desert receives between 100 to 500 mm of rainfall every year, 90% of which is received between July and September. The sandy soils of the desert have a rapid infiltration rate of water, poor fertility, low humus con-tent due to rapid oxidation and high salinity. All conditions are very hostile for the ex-istence of life, yet, large human and livestock populations inhabit the area. The Indian desert is highly fragile with poor primary producers but large liabilities i.e. the con-sumers causing severe impediments in its 'ecological regeneration' and 'desertifica-tion control' efforts.
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Realistic parameterization of land surface processes must take into account heterogeneities in the land surface. In the case of a sparse canopy, interpretation of remotely sensed measurements is very difficult and somewhat questionable in attempts to relate the vegetation indices (VIs) to fractional vegetation cover information. This paper provides an intercomparison of satellite observations at different scales for the purpose of assessing and monitoring vegetation changes at a regional scale. It is designed (1) to evaluate the level of association that can be expected from a model relating basic tools such as spectrally derived VIs from AVHRR and green biomass data for a set of heterogeneous surfaces in a representative semi-arid region and (2) to determine the best strategy for using satellite imagery in that context. The quantitative relationships between radiation data collected in space and characteristics of land surfaces are investigated in the context of the HAPEX-Sahel study over the Niger. A north-south vegetation gradient was accurately located and documented. Corresponding SPOT data, acquired on the same day for the same test site, at 20m spatial resolution were then resampled to the plate carree projection for comparison with National Oceanic and Atmospheric Administration Advanced Very High Resolution Radiometer (NOAA AVHRR) HRPT data (1km spatial resolution). This processing helped in the description and full interpretation of the evolution of various vegetation indices derived from NOAA AVHRR data on these semi-arid regions. One outcome of the data processing is that the resulting relationship between spectral indices and the effective biomass is found to be nonlinear within our low biomass range. When this scheme is applied to NOAA AVHRR data, the Normalized Difference Vegetation Index (NDVI), the Modified Soil-Adjusted Vegetation Index (MSAVI) and the Global Environment Monitoring Index (GEMI) appear to provide detailed information about biomass evolution. However, the accuracy is somewhat different depending on the fractional vegetation cover value. Strategies to estimate information on green biomass in semi-arid regions are different depending on the vegetation index used. In order to use the NDVI or MSAVI properly at the surface level, we have no choice but to perform carefully prepared atmospheric corrections. This data preprocessing is not necessary for the GEMI, which is computed without the need for any atmospheric corrections.
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The paper presents results on the use of NOAA AVHRR data for desertification monitoring on a regional–global level. It is based on processing of the GIMMS 8 km global NDVI data set. Time series of annually integrated and standardized annual NDVI anomalies were generated and compared with a corresponding rainfall data set (1981–2003).The regions studied include the Mediterranean basin, the Sahel from the Atlantic to the Red Sea, major parts of the drylands of Southern Africa, China–Mongolia and the drylands of South America, i.e. important parts of the desertification prone drylands of the world.It is concluded that the suggested methodology is a robust and reliable way to assess and monitor vegetation trends and related desertification on a regional–global scale. A strong general relationship between NDVI and rainfall over time is demonstrated for considerable parts of the drylands. The results of performed trend analysis cannot be used to verify any systematic generic land degradation/desertification trend at the regional–global level. On the contrary, a “greening-up” seems to be evident over large regions.
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The relationship between multi‐year (1989–2003), herbaceous biomass and 1‐km Advanced Very High Resolution Radiometer (AVHRR) Normalized Difference Vegetation Index (NDVI) data in Kruger National Park (KNP), South Africa is considered. The objectives were: (1) to analyse the underlying relationship between NDVI summed for the growth season (ΣNDVI) and herbaceous biomass in field sites (n = 533) through time and (2) to investigate the possibility of producing reliable herbaceous biomass maps for each growth season from the satellite ΣNDVI observations. Landsat Enhanced Thematic Mapper Plus (ETM+) and Thematic Mapper (TM) data were used to identify highly heterogeneous field sites and exclude them from the analyses. The average R for the ΣNDVI–biomass relationship at individual sites was 0.42. The growth season mean biomass and ΣNDVI of most landscape groups were strongly correlated with rainfall and each other. Although measured tree cover and MODIS estimates of tree cover did not have a detectable effect on the ΣNDVI–biomass relationship, other observations suggest that tree cover should not be ignored. The ΣNDVI was successful at estimating inter‐annual variations in the biomass at single sites, but on an annual basis the relationship derived from all the sites was not strong enough (average R = 0.36) to produce reliable growth season biomass maps. This was mainly attributed to the fact that the biomass data were sampled from very small field sites that were not fully representative of 1‐km AVHRR pixels. Supplementary field surveys that sample a larger area for each field site (e.g. 1 km or larger) should account for the variability in biomass and may improve the strength of ΣNDVI–biomass relationships observed in a single growth season.
Data
Time series of rainfall data and normalized difference vegetation index (NDVI) were used to evaluate land cover performance in Senegal, Africa, for the period 1982–1997, including analysis of woodland/forest, agriculture, savanna, and steppe land cover types. A strong relationship exists between annual rainfall and season-integrated NDVI for all of Senegal (r ¼ 0:74 to 0.90). For agriculture, savanna, and steppe areas, high positive correlations portray 'normal' land cover performance in relation to the rainfall/NDVI association. Regions of low correlation might indicate areas impacted by human influence. However, in the woodland/forest area, a negative or low correlation (with high NDVI) may reflect 'normal' land cover performance, due in part to the saturation effect of the rainfall/NDVI association. The analysis identified three areas of poor performance, where degradation has occurred over many years. Use of the 'Standard Error of the Estimate' provided essential information for detecting spatial anomalies associated with land degradation.
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Northern and Southern Hemisphere polar stereographic maps of `vegetation index' are now being produced by the National Oceanic and Atmospheric Administration. The maps are derived from visible and near-infrared data from NOAA's operational polar orbiting satellites. The data are composited over a weekly period to minimize cloud and scan angle effects. The mapped images are being made available to the public in both image and tape format, on a regular schedule.
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A new SVR (Synthetic Variable Ratio) merging method is described which reproduces the spectral characteristics of an original multispectral image and spatial information of a panchromatic image with higher resolution very well. Different TM bands and SPOT pan images in two different large urban areas were used as test data to assess the new SVR method. The spectral and spatial effects of the new SVR method were assessed by using visual and graphical methods and the results were compared with those of the IHS (Intensity, Hue, Saturation) and PCS (Principal Component Substitution) methods. The results show that the spectral effect of the SVR method is the best of the three merging methods. The spatial effect of the SVR method is the same as that of the other two methods.