Sébastien Ollier , Sandrine Pavoine and Pierre...

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1 Comparing and classifying multi-scale spatial patterns Sébastien Ollier * , Sandrine Pavoine and Pierre Couteron Laboratoire de Biométrie et Biologie Evolutive CNRS, UMR 5558, Université Claude Bernard, Lyon1 FRANCE 90 th Annual Meeting (ESA), August 7-12 2005, Montreal, Canada

Transcript of Sébastien Ollier , Sandrine Pavoine and Pierre...

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Comparing and classifyingmulti-scale spatial patterns

Sébastien Ollier*, Sandrine Pavoine and Pierre Couteron

Laboratoire de Biométrie et Biologie EvolutiveCNRS, UMR 5558,

Université Claude Bernard, Lyon1FRANCE

90th Annual Meeting (ESA), August 7-12 2005, Montreal, Canada

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Introduction• Remotely sensed data to understand vegetation/land surface interface

• One sampling unit

PATTERN ANALYSIS

2-D

AutocorelogramFractal dimension

VariogramPeriodogramScalogram...

1-D

VARI

AN

CE

SCALES

kV

k• Many sampling units

1-D

2-D

How to compare many sampling unitson the basis of their spatial patterns?

How to assess the relative importanceof scales in a set of sampling units ?

DALE et al. (2002) Ecography

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I. Pattern quantification1. Two Term Local Variance2. Mean Block Size Variance3. Spectral Analysis

II. Pattern ordination1. Scale standardization2. Ordination by a centred PCA

III.Application to laser profiles1. Data set2. Results

HILL (1973) J. Ecol.

RIPLEY (1978) J. Ecol.

GREIG-SMITH (1952)Ann. bot.

OLLIER et al. (2003)Rem. Sens. Env.

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I. Pattern quantification

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HILL (1973) J. Ecol.

( ) ( ) ( )

( )

2 2 21 1 2 2 3 3 4

1

22 1 2 3 4

2

1

1

ttlv x x x x x xS

ttlv x x x xS

= − + − + −

= + − −

PATTERN ANALYSIS( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

1 4n =

2 2n =

Scalogram

1. Two Term Local Variance

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( )

( )

1 1 2 3 4

2 1 2 2 3 3 4

, , ,

, ,

t

t

x x x x

x x x x x x

=

= + + +

x

x

k k=x H x

1 4

2

1 1 0 00 1 1 00 0 1 1

=

=

H Id

H1

1. Two Term Local Variance

HILL (1973) J. Ecol.

( ) ( ) ( )

( )

2 2 21 1 2 2 3 3 4

1

22 1 2 3 4

2

1

1

ttlv x x x x x xS

ttlv x x x xS

= − + − + −

= + − −

PATTERN ANALYSIS( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

1 4n =

2 2n =

Scalogram

OLLIER et al. (2003)Rem. Sens. Env.

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1 1b =

1

0 1 0 01 0 1 00 1 0 10 0 1 0

M

=

2 2b =

2

0 0 10 0 01 0 0

M =

2

1

1 0 0 00 2 0 00 0 2 00 0 0 1

N

=

2

1 0 00 0 00 0 1

N =

1 2x x+ 2 3x x+ 3 4x x+

1 2 3 4x x x x

1. Two Term Local Variance

( )

( )

1 1 2 3 4

2 1 2 2 3 3 4

, , ,

, ,

t

t

x x x x

x x x x x x

=

= + + +

x

x

k k=x H x

1 4

2

1 1 0 00 1 1 00 0 1 1

=

=

H Id

H1

HILL (1973) J. Ecol.

( ) ( ) ( )

( )

2 2 21 1 2 2 3 3 4

1

22 1 2 3 4

2

1

1

ttlv x x x x x xS

ttlv x x x xS

= − + − + −

= + − −

PATTERN ANALYSIS( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

1 4n =

2 2n =

Scalogram

OLLIER et al. (2003)Rem. Sens. Env.

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3( )t

k k k kk

k

ttlvS−

=x N M x

1. Two Term Local Variance

( )

( )

1 1 2 3 4

2 1 2 2 3 3 4

, , ,

, ,

t

t

x x x x

x x x x x x

=

= + + +

x

x

k k=x H x

1 4

2

1 1 0 00 1 1 00 0 1 1

=

=

H Id

H1

HILL (1973) J. Ecol.

( ) ( ) ( )

( )

2 2 21 1 2 2 3 3 4

1

22 1 2 3 4

2

1

1

ttlv x x x x x xS

ttlv x x x xS

= − + − + −

= + − −

PATTERN ANALYSIS( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

1 4n =

2 2n =

Scalogram

OLLIER et al. (2003)Rem. Sens. Env.

1 1b =

1

0 1 0 01 0 1 00 1 0 10 0 1 0

M

=

2 2b =

2

0 0 10 0 01 0 0

M =

2

1

1 0 0 00 2 0 00 0 2 00 0 0 1

N

=

2

1 0 00 0 00 0 1

N =

1 2x x+ 2 3x x+ 3 4x x+

1 2 3 4x x x x

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1 1b =

2 2b = 1 2x x+ 3 4x x+

1 2 3 4x x x x

( )

ttlv witht

kk

kt

k k k k k

S=

= −

x A x

A H N M H

1. Two Term Local Variance

HILL (1973) J. Ecol.

( ) ( ) ( )

( )

2 2 21 1 2 2 3 3 4

1

22 1 2 3 4

2

1

1

ttlv x x x x x xS

ttlv x x x xS

= − + − + −

= + − −

PATTERN ANALYSIS( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

1 4n =

2 2n =

Scalogram

OLLIER et al. (2003)Rem. Sens. Env.

3( )t

k k k kk

k

ttlvS−

=x N M x

( )

( )

1 1 2 3 4

2 1 2 2 3 3 4

, , ,

, ,

t

t

x x x x

x x x x x x

=

= + + +

x

x

k k=x H x

1 4

2

1 1 0 00 1 1 00 0 1 1

=

=

H Id

H1

2

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2. Mean Block Size Variance

GREIG-SMITH (1952)Ann. bot.

( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

3 4b =

1 4n =

2 2n =

3 1n =

( ) ( )

( )

2 21_ 2 1 2 3 4

1

22_ 4 1 2 3 4

2

1 1 12 2

1 14

msbs x x x xS

msbs x x x xS

= − + −

= + − −

PATTERN ANALYSIS

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( )

( )

( )

1 1 2 3 4

2 1 2 1 2 3 4 3 4

3 1 2 3 4 1 2 3 4

, , ,

, , ,

, ... ,

t

t

t

x x x x

x x x x x x x x

x x x x x x x x

=

= + + + +

= + + + + + +

x

x

x

tk k=x H x1

_ 1 1 11

1 1k k k k k k

k kb b+ + ++

= −y H x H x

2

1 2

2 1

3 4

4 3

12

x xx xx xx x

− − − −

1 2 3 4

1 2 3 4

3 4 1 2

3 4 1 2

14

x x x xx x x xx x x xx x x x

+ − − + − − + − − + − −

1 4

2

3 4 4

1 1 0 01 1 0 00 0 1 10 0 1 1t

=

=

=

H Id

H

H 1 1

1_ 2y 2_ 4y

3_ 1 _ 1 _ 1t

k k k k k kmsbs + + += y y

2. Mean Block Size Variance

GREIG-SMITH (1952)Ann. bot.

( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

3 4b =

1 4n =

2 2n =

3 1n =

( ) ( )

( )

2 21_ 2 1 2 3 4

1

22_ 4 1 2 3 4

2

1 1 12 2

1 14

msbs x x x xS

msbs x x x xS

= − + −

= + − −

PATTERN ANALYSIS

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_ 1_ 1

1 1 1 11 1

msbs with

1 1 1 1

tk k

k kk

t t t tk k k k k k k k k

k k k k

S

b b b b

++

+ + + ++ +

=

= − −

x A x

A H H H H H H H H

( )

( )

( )

1 1 2 3 4

2 1 2 1 2 3 4 3 4

3 1 2 3 4 1 2 3 4

, , ,

, , ,

, ... ,

t

t

t

x x x x

x x x x x x x x

x x x x x x x x

=

= + + + +

= + + + + + +

x

x

x

tk k=x H x1

_ 1 1 11

1 1k k k k k k

k kb b+ + ++

= −y H x H x

2

1 2

2 1

3 4

4 3

12

x xx xx xx x

− − − −

1 2 3 4

1 2 3 4

3 4 1 2

3 4 1 2

14

x x x xx x x xx x x xx x x x

+ − − + − − + − − + − −

1_ 2y 2_ 4y

3_ 1 _ 1 _ 1t

k k k k k kmsbs + + += y y

2. Mean Block Size Variance

GREIG-SMITH (1952)Ann. bot.

( )1 2 3 4, , ,t x x x x=x

1 1b =

2 2b =

3 4b =

1 4n =

2 2n =

3 1n =

( ) ( )

( )

2 21_ 2 1 2 3 4

1

22_ 4 1 2 3 4

2

1 1 12 2

1 14

msbs x x x xS

msbs x x x xS

= − + −

= + − −

PATTERN ANALYSIS

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3.Spectral analysis

RIPLEY (1978) J. Ecol.

( )1 2 3 4, , ,t x x x x=x

( ) ( ) ( )

( ) ( )

2 2

1 1 11 11

2

2 212

1 1 cos sin

1 1 cos

n n

i ii i

n

ii

I x i x iS n

I x iS n

ω ω ω

ω ω

= =

=

= +

=

∑ ∑

1k =

1k =1

2nπω =

2k =2ω π=

Periodogramcos

cos

sin

1c

1s

2c

PATTERN ANALYSIS

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( )

( )

I with

1

tk

kk

t tk k k kk

S

n

ω =

= +

x A x

A c c s s

3.Spectral analysis

RIPLEY (1978) J. Ecol.

( )1 2 3 4, , ,t x x x x=x

( ) ( ) ( )

( ) ( )

2 2

1 1 11 11

2

2 212

1 1 cos sin

1 1 cos

n n

i ii i

n

ii

I x i x iS n

I x iS n

ω ω ω

ω ω

= =

=

= +

=

∑ ∑

1k =

1k =1

2nπω =

2k =2ω π=

Periodogramcos

cos

sin

1c

1s

2c

PATTERN ANALYSIS

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Pattern quantificationMean square block size analaysis

Two term local varance

Spectral analysis

1-D

VARI

AN

CE

SCALES

kV

k

1-D

...

• Many sampling units

• One sampling unit Vt

kk

kS=

x A x

TABLE Z

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How to choose the scaling coeficient ?

Pattern quantificationMean square block size analaysis

Two term local varance

Spectral analysis

1-D

VARI

AN

CE

SCALES

kV

k

1-D

...

• Many sampling units

• One sampling unit Vt

kk

kS=

x A x

TABLE Z

kS

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II. Pattern ordination

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1. Scale standardization

EUCLIDEAN STANDARDIZATION

( )k kS trace A=

• Two term local variance

161, 2, 4,8

nk==

kS

1k = 2 4 8

30 52 72 16

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1. Scale standardization

EUCLIDEAN STANDARDIZATION SPECTRAL STANDARDIZATION

( )k kS trace A= ( )1k kS Aλ=

• Two term local variance

161, 2, 4,8

nk==

kS

1k = 2 4 8

30 52 72 16 kS

1k = 2 4 84 9 26 16

firsteigenvectors

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1. Scale standardization

EUCLIDEAN STANDARDIZATION SPECTRAL STANDARDIZATION

( )k kS trace A= ( )1k kS Aλ=

• Two term local variance

161, 2, 4,8

nk==

kS

1k = 2 4 8

30 52 72 16 kS

1k = 2 4 84 9 26 16

• Mean block size variance

kS 8 4 2 1

• Spectral analysis

kS 2 2 2 1

kS 1 1 1 1

kS 1 1 1 1

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2.Ordination by a centred PCA

SCALES

1-D

...

TABLE Z

Vk values

TRA

NSE

CTS Centered

PrincipalComponentAnalysis

1

p

q...

...• Eigenvalues

• Coordinates onPrincipal Components

• Coordinates onPrincipal Axes

Package ade4 : http://pbil.univ-lyon1.fr/ADE-4Software R : http://cran.univ-lyon1.fr/R

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III. Application

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1. Data set

OLLIER et al. (2003) Rem. Sens. Env.

N

E

S

O

N

E

S

O

The study site

2.5 km

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1. Data set

N

E

S

O

N

E

S

O2.5 km

The study site

• ALLUVIAL PLAINSvery simple

and flat relief

• COMPLEX RELIEF FORMS< 60 m

gently slopes

• COMPLEX RELIEF FORMS> 60 m

steep slopesC

A

B

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1. Data set

N

E

S

O

N

E

S

O2.5 km

The study site

• ALLUVIAL PLAINSvery simple

and flat relief

• COMPLEX RELIEF FORMS< 60 m

gently slopes

• COMPLEX RELIEF FORMS> 60 m

steep slopes

A

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1. Data set

N

E

S

O

N

E

S

O2.5 km

The study site

• ALLUVIAL PLAINSvery simple

and flat relief

• COMPLEX RELIEF FORMS< 60 m

gently slopes

• COMPLEX RELIEF FORMS> 60 m

steep slopes

A

B

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1. Data set

N

E

S

O

N

E

S

O2.5 km

The study site

• ALLUVIAL PLAINSvery simple

and flat relief

• COMPLEX RELIEF FORMS< 60 m

gently slopes

• COMPLEX RELIEF FORMS> 60 m

steep slopes

B

A

C

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1. Data set

N

E

S

O

N

E

S

O2.5 km

Laser data

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1. Data set

264 laser transects

N

E

S

O

N

E

S

O2.5 km

264 laser transects (n=64)

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Pattern analysis and ordination

264 scalograms (block size = 1,2,4,8,16,32)

264 laser transects (n=64)

TTLV

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Pattern analysis and ordination

264 scalograms (block size = 1,2,4,8,16,32)

264 laser transects (n=64)

TTLVPCA

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2.Results

• Eigenvalues

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d = 0.2

ttg_1 ttg_2

ttg_4

ttg_8 ttg_16

ttg_32

2.Results

• Eigenvalues

• Principal axis

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d = 0.2

ttg_1 ttg_2

ttg_4

ttg_8 ttg_16

ttg_32

2.Results

• Coordinates on principal components

• Eigenvalues

• Principal axis

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35

d = 0.2

1 2 3

4

5 ttg_1 ttg_2

ttg_4

ttg_8 ttg_16

ttg_32

2.Results

• FIVE CLUSTERS• Coordinates on principal components

• Eigenvalues

• Principal axis

Page 36: Sébastien Ollier , Sandrine Pavoine and Pierre Couteronbiol09.biol.umontreal.ca/ESA_SS/Ollier_et_al_talk.pdf · bbkk + ++ + yHxHx=− 2 12 21 34 43 1 2 x x x x x x x x − − −

36

d = 0.2

1 2 3

4

5 ttg_1 ttg_2

ttg_4

ttg_8 ttg_16

ttg_32

2.Results

• FIVE CLUSTERS• Coordinates on principal components

• Eigenvalues

• Principal axis

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

1 23

4

5

Page 37: Sébastien Ollier , Sandrine Pavoine and Pierre Couteronbiol09.biol.umontreal.ca/ESA_SS/Ollier_et_al_talk.pdf · bbkk + ++ + yHxHx=− 2 12 21 34 43 1 2 x x x x x x x x − − −

37

d = 0.2

1 2 3

4

5 ttg_1 ttg_2

ttg_4

ttg_8 ttg_16

ttg_32

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

ttg_1 ttg_2 ttg_4 ttg_8 ttg_16 ttg_32

0.0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

1 23

4

5

2.Results

9191248C

234223248B

186752A54321

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38

Conclusion

• An efficient method to summarizeand classify 1-D spatial patterns

• A very general approach

• Generalization to 2-D sampling unitsCOUTERON et al. (2005) J. Appl. Ecol.