Segmentacion
• Tecnica no supervisada que intenta
particionar (segmentar) a los individuos (casos) de modo tal que los grupos
formados sean heterogeneos entre si y
Objetivos
• Obtener una representación “compacta” de los datos, para:
– Generar una clasificación – Describir los datos
– Definir “prototipos” de interes. – Resumir la infprmación.
Sin Clusterización
X1 X2
Con Clusterización
X1 X2
Complejidad del problema
Para K=3 y N=30 P(N,K)= 2 * 1014 Cantidad de objetos Cantidad de clusters Cantidad de segmentaciones posiblesEjemplo de Espacio Métrico
M
x
y z
Métricas
• Datos continuos: Distancia Euclidea
Distancia Chi Cuadrado
Distancia Proporción promedio marginal de la variable j Las J proporciones de la observación X Las J proporciones de la observación YDos tipos de segmentacion
• Metodos jerarquicos
– Ascendentes o Aglomerativos – Decendentes o de Difusión
• Metodos no jerarquicos o de particion
– K medias – PAM
Ejemplo
Definiciones
Objetos Dimensión del espacio Cantidad de grupos Partición Disjuntos TotalidadMétodos Jerarquicos
• Producen un “continuo” de particiones jerarquicas facilmente visualizable
mediante un dendograma.
• Dependen de dos nociones de similaridad :
– Entre objetos. – Entre clusters.
• No necesitan definir una cantidad de grupos “a priori”.
Métodos Jerárquicos (HC)
Descendente Ascendente
Jerarquia de particiones
Objetos Particiones
Método
Ascendente
INICIO 1 IND. = 1 CLUST. MATRIZ DIST. UNIR 2 CLUSTERS 1 CLUSTER ? SI NO CORTAR EL DENDOGRAMA FINMatriz de Distancias
C1 … Cl Ci Cj … Cn C1 0 … Cl 0 D(Cl,Ci) D(Cl,Cj) Ci D(Cl,Ci) 0 D(Ci,Cj) Cj D(Cl,Ci) … D(Cl,Cj) D(Ci,Cj) 0 … D(Cl,Cn) … Cn 0Recalculo de la Matriz de
Distancias
C1 … Cl Ci,j … Cn C1 0 … Cl 0 D(Cl,Ci,j)Ci,j D(Cl,Ci,j) D(Cl,Ci,j) 0 D(Cn,Ci,j) …
Distancia entre clusters: Single
linkage
Distancia entre clusters:
Complete Linkage
Distancia entre clusters:
Average
Desventajas de HC
• Costoso en grandes bases de datos. • Es lento.
Ventajas de HC
• Sugiere el número de clusters.
• Establece una jerarquía de clusters.
• El dendograma permite la visualización del proceso.
Métodos de Partición o
Combinatorios
• Producen grupos (clusters) mediante el agrupamiento de objetos situados en
lugares cercanos del espacio al que petenecen.
• Dependen de la existencia de coordenadas de los objetos.
• Requieren definir la cantidad de grupos. • Requieren definir una función de perdida.
Criterio del ECM
Dado un conjunto de objetos queremos
agruparlos en La suma de errores al
cuadrado se define como:
Donde
es una matriz
cc si
es la matriz de prototipos o centroides es la media muestral
Otros criterios
Diametro del Cluster Star index
Radio del Cluster Cut index
K-Medias (Paso 0)
K-Medias (Paso 1)
K-Medias (Paso 2)
Clusters determinados por los centros
K-Medias (Paso 3)
K-Medias (Paso 4)
Nuevos clusters
K-Medias (Paso 5)
Desventajas de K-medias
• Converge a un optimo local (no global). • La clusterización final depende de los
centros iniciales.
• Requiere fijar el número de clusters previamente.
Ventajas de K-medias
• Es rápido.
Métodos Mixtos
• Consisten en aplicar:
– Primero: Un método combinatorio (k-medias) con una cantidad de clusters grande (K=200). – Segundo: Un método jerarquico al resultado
del método combinatorio. Es decir, se unen los clusters hallados en el primer método.
Así, los clusters finales consisten en la unión de los objetos pertenecientes a los clusters
Dendograma
2 Clusters
3 Clusters
Mean Shift
• Técnica basada en KDE
• Se originó como un método tipo “hill-climbing” para “Bump Hunting”
• Permite captar clusters con “formas” complejas
• Es (relativamente) lento
• Obedece a un enfoque no-paramétrico
La Idea: Mean Shift como
método de Bump Hunting
Media Punto
Desplazamiento hacia la media
Media Punto
Convergencia
Moda de la densidad
Calculando el
Mean Shift
Clustering con Mean Shift
Se sigue (con MS) cada objeto hasta su convergencia
Cluster 1
Cluster 2 Todos los objetos que convergen al mismo punto pertenecen al mismo cluster
Propiedades
• Convergencia asegurada para todos los objetos
• Cantidad de clusters dependiente de la ventana en la KDE
Ventana grande -> 1 Cluster Ventana chica -> 2 Clusters
Usando una Ventana Grande
(ventana = 50% rango)
Using unaa Ventana Chica
(ventana = 35% rango)
Determinación del número de
clusters
• Criterio de Clusterización Cúbico de
Sarle (CCC).
• Estadístico GAP.
• Estadístico Psuedo-F
Validación de los clusters
• Criterios externos: Comparan la
clusterización con algúna segmentación previa de referencia.
• Criterios internos: Analizan la
significatividad de los clusters solo considerando los datos usados en la clusterización.
• Criterios relativos: Comparan la
clusterización con otras resultantes de segmentaciones alternativas.
El Estadístico Pseudo F
(Calinkski-Harabasz)
Media general Media cluster i K clusters Cantidad de ObjetosEstadístico GAP
Distancias WITHIN observadas Distancias WITHIN esperadas bajo H0 (K=1) Cantidad optima de clusters clusGapFeature Spaces Complejos
• El espacio de covariables puede ser tan complejo como se quiera.
• Se pueden definir nuevos features que
capten comportamientos diferenciales del fenómeno.
• Es fundamental la ponderación que se da a cada feature.
Automatic and Extensive
Cropland Classification Based on
Satellite Data
Why Automatic Crop
Classification ?
• Crops in Argentina: ~ 34.000.000 has, ~
400.000 fields
• Screening of unknown regions
• Global yield estimation and tax evasion
control
• Valuable information for agro-related and
agro-insurance companies
• Precise georeference of croplands
• Global crop area assesment and yield
Some Specific Classification
Goals
• To assess crop share (relative proportions) in a
large area (no georeference available of the fields) • To estimate yield of an specific crop/season in a
large area (no georeference available of the fields) • To detect and to georeference fields with specific
crops (no georeference available of the fields) • To detect kind-of-crop info from specific fields
Kind of Crops to be Detected
• Arable land – Summer crops • Soybean • Corn – Winter crops • Wheat • Sunflower• Non arable land
Very easy Easy
Hard Hard
Remote Sensing Instruments
LON LA T NIR Band Red Band … … … … … … … … … … …● ID Tas 3293 Estado 18 Has 8 Danio 3.4 Lat −31.8573 Lon −61.7189 Fec Sin 2012−12−19 10:10:00 ID Sin 876 Fec Siem 2012−10−30 16:33:00
Main Available Remote Sensing
Instruments
• MODIS (MODerate Imaging Spectrometer) – 250m X 250m
– 2 images per day
– 2 satellites (Terra and Aqua) – 36 spectral bands
• LANDSAT 8
– 15m X 15m (interpolated)
– 1 image every 16 days – 1 satellite
Vegetation Indices (VIs)
• CI • EVI • ENVI • NDVI Source: http://www.markelowitz.com Wavelength -1 ≤ NDVI ≤ 1 0 ≤ NDVI ≤ 1 For plants In general R ef le ct ed In te nsi tyHow is a Typical Phenological Crop
Cycle ?
Nov Jan Mar May Jul
0.0 0.2 0.4 0.6 0.8 1.0
Evolucion del cultivo
Tiempo ND VI ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ●● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ●● ● ● ● ●● ● ● ● ● ● ● ● ● ●● ●● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●●● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ●● Start of season Time End of season Maturity of the plant Daily (2) NDVI measurements Soybea n cycle Terra measurement Aqua measurement
Double-Crop Phenological Cycle
May Jul Sep Nov Jan Mar May
0.0 0.2 0.4 0.6 0.8 1.0
Evolucion del cultivo
Tiempo ND VI ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ●●● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ●● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ● ● ● ● ● ●● ● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●● ●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● Time Winter crop Summe rcrop Terra measurement Aqua measurement
Landsat: Big Data !
Argentina China
Landsat tile = 185km X 185 km ~
Cropland Detection Using Landsat
8
Unsupervised Approach
● −59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 NDVI image (2014−10−16) 0.2 0.3 0.4 0.5 0.6 0.7 0.8 ●Visible image from
Open Street Map NDVI image
(2014-10-16) Point of
● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● 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● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ●●●● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● 1 3 5 7 9 11 13 15 17 19 21 23 25 0.2 0.4 0.6 0.8 NDVI distribution ND VI −59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 NDVI clustering 5 10 15 20 25 ●
Single Image Clustering
based on X + Y + NDVI
−59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 0.2 0.3 0.4 0.5 0.6 0.7 0.8 Feature space 25 ClustersThe Feature Space
X + Y + NDVI
Field of interest
Field Detected
● −59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 5 10 15 20 25 Clusters of similar NDVI valuesPolygon induced by the method
Actual
georeferenced field
−59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 0.2 0.3 0.4 0.5 0.6 0.7 0.8 −59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Time series of Landsat images
● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● ● 0.1 0.2 0.3 0.4 0.5 0.6
NDVI evoliution (LAndsat)
Time
ND
VI
Sep 14/2014 Nov 17/2014 Jan 20/2015 Mar 25/2015 May 28/2015 Jul 31/2015 Oct 03/2015
● ● ● ● ● ● ● ● ● ● ● −59.10 −59.09 −59.08 −59.07 −59.06 − 37.73 − 37.72 − 37.71 − 37.70 0.12 0.13 0.14 0.15 0.16 Cloudy image Freshly sowed field Crop close to maturity
Whole image NDVI evolution
Cloudy Clear sky
Working With a Temporal Ensemble of
Images
Time N D VI ● Pixel 2 NDVI evolution NDVIpx = µpx + αpx * Time+ βpx * Time2 Pixel-wise modellingAdded Attributes Based on Statistical
Modelling of NDVI Temporal Evolution
0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 NDVIpx = µpx + αpx * Time + βpx * Time2 ^ ^ ^ Pixel-wise modelling F alse co lo r ima ge
Clustering Based on Modelled
NDVI Temporal Evolution
−37.75 −37.74 −37.73 −37.72 −37.71 −37.70 −37.69 −59.09 −59.08 −59.07 −59.06 5 10 15 20 25 Time N D VI 25 NDVI estimated evolutions 25 clusters 2 4 6 8 10 0.1 0.2 0.3 0.4 0.5 0.6 0.7 x 1:11 Field of interest Feature space X +Y +µ + α + β