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Urbaniza(on can bring improvements to social welfare and economic development. However, it can also have serious impacts on the natural environment, both locally and globally (Grimm et al. 2008). Also, it is arguably the most dras(c form of land transforma(on, which results in irreversible landscape changes (Estoque and Murayama 2014). In the context of landscape and urban studies, the analysis of the intensity and spa(al paKern of urban land changes (ULCs) might be of help, as it can give some insights about the spa(otemporal paKern of future ULCs, including their poten(al environmental impact. The purpose of this study is to examine and compare the intensity and spa(al paKern of ULCs in three major ci(es of Southeast Asia, namely Bangkok (Thailand), Jakarta (Indonesia) and Manila (Philippines), between the 1990s (1990‐2000) and 2000s (2000‐2010). Land‐cover classifica2on: Image data – Landsat imageries Time points – 1990, 2000 and 2010 Approach – Random Forest image classifica(on approach (Liaw 2002; R Core Team 2012). Land change intensity (LCI) analysis (interval): – examines how the size and annual rate of change vary across (me intervals (Aldwaik and Pon(us 2012). In this study, it was done by: 1) calcula(ng the annual change intensity (ACI) for each (me interval (TI) (Eq. 1); 2) deriving the uniform intensity (UI) (Eq. 2); 3) determining the intensity category level (CL) value (Eq. 3); 4) applying the proposed LCI scale (Fig. 2). The ULCs (1990s‐2000s) in the three ci(es were spa(ally and temporally non‐sta(onary. The LCI analysis approach might help in the study of the drivers of ULCs. It can also be used as a diagnos(c tool for evalua(ng land change projec(ons. The three ci(es have been experiencing an infilling urban development paKern. Infilling paKern, if not monitored and controlled, can result to the loss of valuable urban green and open spaces. Aldwaik SZ, Pon(us RG, Jr. 2012. Landscape and Urban Planning 106: 103‐114. Estoque RC, Murayama Y. 2014. AMBIO 43: 943–956. Grimm, N. B., et al. 2008. Science 319: 756–760. Liaw A, Wiener M. 2002. R News 2: 18–22. McGarigal K, et al. 2012. FRAGSTATS v4: Spa2al paKern analysis program. R Core Team. 2012. R: A language and environment for sta2s2cal compu2ng. Ronald C. ESTOQUE* and Yuji MURAYAMA Division of Spa(al Informa(on Science, Faculty of Life and Environmental Sciences University of Tsukuba, 1‐1‐1 Tennodai, Tsukuba City, Ibaraki 305‐8572, Japan *Contact email address: <[email protected]> Fig. 1. Flowchart of the study. Note: B = Bangkok; J = Jakarta; M = Manila Fig. 3. CL values: 1988‐1999 = ‐10.42 (medium slow); 1999‐2009 = 11.46 (medium fast). D05 Poster presented during the CSIS Days 2014, November 21‐22, 2014, Chiba, Japan. Fig. 2. Land change intensity (LCI) scale. Key (others, refer to the text) : LC = land change From Non‐built To Built LA = landscape area TE = (me extent Spa2al paKern analysis: The density of urban development along the gradient of the distance from the city center, and the patch cohesion index, which determines the level of physical connectedness of the corresponding patch type (e.g. built) (McGarigal et al. 2012), were determined. From Non‐built To Built Bangkok Fig. 4. CL values: 1989‐2001 = 19.23 (medium fast); 2001‐2010 = ‐25.64 (slow). Jakarta Fig. 5. CL values: 1993‐2001 = 6.16 (medium fast); 2001‐2009 = ‐6.16 (medium slow). Manila From Non‐built To Built From Non‐built To Built 0 20 40 60 80 100 2009 1999 1988 DoUD (%) Bangkok 0 20 40 60 80 100 2010 2001 1989 0 20 40 60 80 100 0‐1.5 1.5‐3.0 3.0‐4.5 4.5‐6.0 6.0‐7.5 7.5‐9.0 9.0‐10.5 10.5‐12.0 12.0‐13.5 13.5‐15.0 15.0‐16.5 16.5‐18.0 2009 2001 1993 Intensity of urban land changes (temporal) SpaNal paOern of urban land changes Fig. 6. Density of urban development (DoUD) along the gradient of the distance from the city center. Note: The area of the water class was not included in the calcula(on. Fig. 7. Patch cohesion index of the built class. Note: Values that are close to zero indicate fragmenta(on, while values that are close to 100 indicate aggrega(on. Jakarta Manila DoUD (%) DoUD (%) Distance from the city center (km) (Eq. 1) (Eq. 2) (Eq. 3)

Ronald C. ESTOQUE* and Yuji MURAYAMA - 筑波大学giswin.geo.tsukuba.ac.jp/sis/poster/2014CSIS_RCEstoque.pdf · Urbanizaon can bring improvements to social welfare and economic development

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Urbaniza(on can bring improvements to social welfare and economic development. However, it can also have serious impacts on the naturalenvironment,bothlocallyandglobally(Grimmetal.2008).Also,itisarguablythemostdras(cformoflandtransforma(on,whichresultsinirreversiblelandscapechanges(EstoqueandMurayama2014).Inthecontextoflandscapeandurbanstudies,theanalysisoftheintensityandspa(alpaKernofurban landchanges (ULCs)mightbeofhelp,as it cangivesome insightsabout thespa(otemporalpaKernof futureULCs, including theirpoten(alenvironmentalimpact.Thepurposeofthisstudyistoexamineandcomparetheintensityandspa(alpaKernofULCsinthreemajorci(esofSoutheastAsia,namelyBangkok(Thailand),Jakarta(Indonesia)andManila(Philippines),betweenthe1990s(1990‐2000)and2000s(2000‐2010).

Land‐coverclassifica2on:• Imagedata–Landsatimageries• Timepoints–1990,2000and2010• Approach–RandomForestimageclassifica(onapproach(Liaw2002;RCoreTeam2012).

Landchangeintensity(LCI)analysis(interval):– examines how the size and annual rate ofchange vary across (me intervals (Aldwaik andPon(us2012).Inthisstudy,itwasdoneby:1) calcula(ngtheannualchangeintensity(ACI)foreach(meinterval(TI)(Eq.1);

2) derivingtheuniformintensity(UI)(Eq.2);3) determiningtheintensitycategory level(CL)value(Eq.3);

4) applyingtheproposedLCIscale(Fig.2).

•  TheULCs(1990s‐2000s)inthethreeci(eswerespa(allyandtemporallynon‐sta(onary.•  TheLCIanalysisapproachmighthelpinthestudyofthedriversofULCs.Itcanalsobeusedasadiagnos(ctoolforevalua(nglandchangeprojec(ons.•  Thethreeci(eshavebeenexperiencinganinfillingurbandevelopmentpaKern.InfillingpaKern,ifnotmonitoredandcontrolled,canresulttothelossofvaluableurbangreenandopenspaces.

•  AldwaikSZ,Pon(usRG,Jr.2012.LandscapeandUrbanPlanning106:103‐114.•  EstoqueRC,MurayamaY.2014.AMBIO43:943–956.•  Grimm,N.B.,etal.2008.Science319:756–760.•  LiawA,WienerM.2002.RNews2:18–22.•  McGarigalK,etal.2012.FRAGSTATSv4:Spa2alpaKernanalysisprogram.•  RCoreTeam.2012.R:Alanguageandenvironmentforsta2s2calcompu2ng.

RonaldC.ESTOQUE*andYujiMURAYAMA DivisionofSpa(alInforma(onScience,FacultyofLifeandEnvironmentalSciences

UniversityofTsukuba,1‐1‐1Tennodai,TsukubaCity,Ibaraki305‐8572,Japan *Contactemailaddress:<[email protected]>

Fig.1.Flowchartofthestudy.Note:B=Bangkok;J=Jakarta;M=Manila

Fig.3.CLvalues:1988‐1999=‐10.42(mediumslow);1999‐2009=11.46(mediumfast).

D05PosterpresentedduringtheCSISDays2014,November21‐22,2014,Chiba,Japan.

Fig.2.Landchangeintensity(LCI)scale.

Key(others,refertothetext):LC=landchangeFromNon‐builtToBuiltLA=landscapeareaTE=(meextent

Spa2al paKern analysis: The density of urbandevelopmentalongthegradientofthedistancefrom the city center, and the patch cohesionindex, which determines the level of physicalconnectednessofthecorrespondingpatchtype(e.g. built) (McGarigal et al. 2012), weredetermined.

FromNon‐builtToBuilt

Bangkok

Fig.4.CLvalues:1989‐2001=19.23(mediumfast);2001‐2010=‐25.64(slow).

Jakarta

Fig.5.CLvalues:1993‐2001=6.16(mediumfast);2001‐2009=‐6.16(mediumslow).

Manila

FromNon‐builtToBuilt

FromNon‐builtToBuilt

0

20

40

60

80

100

2009 1999 1988DoU

D(%

) Bangkok

0

20

40

60

80

100

2010 2001 1989

020406080100

0‐1.5

1.5‐3.0

3.0‐4.5

4.5‐6.0

6.0‐7.5

7.5‐9.0

9.0‐10.5

10.5‐12.0

12.0‐13.5

13.5‐15.0

15.0‐16.5

16.5‐18.0

2009 2001 1993

Intensityofurbanlandchanges(temporal) SpaNalpaOernofurbanlandchanges

Fig. 6. Density of urban development (DoUD) along the gradient of thedistance from the city center. Note: The area of the water class was notincludedinthecalcula(on.

Fig. 7. Patch cohesion index of thebuilt class. Note: Values that areclosetozeroindicatefragmenta(on,while values that are close to 100indicateaggrega(on.

Jakarta

Manila

DoU

D(%

)DoU

D(%

)

Distancefromthecitycenter(km)

(Eq.1)

(Eq.2)

(Eq.3)