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Statistical Approaches for Un-Mixing Problem and
Application to Satellite Remote Sensing Data
Zhengyuan Zhu
Joint work with Remote Sensing Sptail Y working group
May 14, 2018
short name May 14, 2018 1 / 30
Spatial Y Working Group Active Members
Jenny Brynjarsdottir (Case Western University)
Xinyue Chang (Iowa State University)
Maggie Johnson (SAMSI, NCSU)
Jon Hobbs (JPL)
Colin Lewis-Beck (Iowa State University)
Anirban Mondal (Case Western University)
Joon Jin Song (Baylor University)
Zhengyuan Zhu (Iowa State University)
short name May 14, 2018 2 / 30
1 Introduction: OCO-2 and SMOS data
2 Parametric un-mixing
3 Non-parametric un-mixing
4 Gap-filling Hyperspectral OCO-2 data
short name May 14, 2018 3 / 30
Motivation: Improve the retrieval of OCO-2 Data
34.50
34.75
35.00
35.25
24.0 24.1 24.2
longitude
latitude
short name May 14, 2018 4 / 30
OCO-2 Data
0.0e+00
3.0e+19
6.0e+19
9.0e+19
1.2e+20
250 500 750
wavelength
meanradiancefunction
pixel
1
2
3
4
5
6
7
8
short name May 14, 2018 5 / 30
Spatial X vs Spatial Y
Spatial X: Model the retrieval variable (X) as spatial process to
improve the retrivel.
Spatial Y: Develop spatial-temporal functional model for the
hyper-spectral reflectance data (Y) to improve retrieval by
Gap-filling the missing data, i.e., impute Y and provide uncertainty of
the imputation.
Smoothing to reduce the noise in Y.
Un-mixing the pixel with mixed land cover (i.e., transition between
water and land).
short name May 14, 2018 6 / 30
Focus on Un-mixing problem
What is un-mixing?
Disregarding atmospheric effects, the signal recorded by the remote
sensing instrument at a pixel is typically a mixture of light scattered by
substances located in the field of view.
Unmixing refers to any process that separates the pixel measurments
from an image into a collection of endmembers and a set of fractional
abundances.
Endmembers: Represent the pure materials present in the image
Abundances: Represent the percentage of each endmember that is
present in the pixel.
The group decided to focus on the un-mixing problem, which will be
the focus of this report.
At the end we also report some preliminary results on gap-filling for
OCO-2.
short name May 14, 2018 7 / 30
Another (Simpler) Motivating Example: SMOS Data
2011 - 2017 on 30 footprints (45 km diameter) in northwest Iowa
Between 75 - 85 % of footprints devoted to annual crops
Satellite makes a pass approximately every 12 - 36 hours at the
midlatitudes
Approximately 60% of each footprint is planted in corn, and 40%
soybean
1 2 3
4
5
6
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10
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16
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29
30
short name May 14, 2018 8 / 30
SMOS Data
Pix 25 2015 Pix 25 2017
Pix 6 2015 Pix 6 2017
M
ay
1
June
1
July
1
Aug
1
Sept1
O
ct1
N
ov
1
M
ay
1
June
1
July
1
Aug
1
Sept1
O
ct1
N
ov
1
0.0
0.2
0.4
0.6
0.0
0.2
0.4
0.6
Month
T
Figure 1: Two representative SMOS pixels.
short name May 14, 2018 9 / 30
Motivating Problem
Crop-specific peak is of interest in agriculture.
SMOS measurements are largely a mixture of corn and soybean signal
in Iowa.
Can we develop a model to un-mix SMOS satellite signal into two
crop types: corn and soybean?
Ground based auxiliary data available to inform the signature of each
crop type
Objective: Reconstruct crop-specific curves using the model and
quantify measures of uncertainty for each crop signal
short name May 14, 2018 10 / 30
Auxiliary Data
Field level data based on experiments in Mead, Nebraska. Shape of corn
and soybean is based on growing degree days (GDD).
Figure 2: Hornbuckle et al. (2016)
short name May 14, 2018 11 / 30
1 Introduction: OCO-2 and SMOS data
2 Parametric un-mixing
3 Non-parametric un-mixing
4 Gap-filling Hyperspectral OCO-2 data
short name May 14, 2018 12 / 30
Data Model: Parametric approach
We translate the SMOS time scale to GDD using ground based
temperature data and crop planting dates.
We model τ as a function of GDD from using an asymmetric Gaussian
(AG) function, a frequently used function to model nonlinear vegetation
data.
fAG
θ (d) =



β + (η − β)exp −(d−δ)2
2σ2
1
d ≤ δ
β + (η − β)exp −(d−δ)2
2σ2
2
d > δ
short name May 14, 2018 13 / 30
Unmixing Model
The Cropland Data Layer from the NASS provides the proportion of corn
and soybean within each region. Let the proportion for the two dominate
crops by defined as: πc (corn), πb (soybean). We assume a common
intercept (γ) to capture the remaining ground vegetation that is constant
over time.
Let r = 1 . . . R denote pixel regions, s = 1 . . . S seasons, and d = 1 . . . D
denote GDD. For a given curve Xrs(d),
xrs(d) = γrs + πcrsfAG
θ1
(d) + πbrsfAG
θ2
(d) + rs(d) rs(d)
ind.
∼ N(0, σrs)
short name May 14, 2018 14 / 30
Unmixing Model
Assuming the curves are exchangeable, and the signatures for corn and
soybean are independent, we an model the parameters hierarchically. Let
µj = (µηj , µδj
, µσ1j, µσ2j) denote the vector of means for the jth mixture
component. We will model these parameters as coming from a
multivariate normal distribution and work with the transformed vector
µθj
= (logit(µηj ), log(µδj
), log(µσ1j), log(µσ2j))
θ1rs
ind.
∼ N4(µθ1 , Σ1)
θ2rs
ind.
∼ N4(µθ2 , Σ2)
logit(γrs)
ind.
∼ N(µγ, τγ)
We put informative priors on the parameter vectors based on MLE
estimates of the AG parameters derived from the Nebraska field data.
short name May 14, 2018 15 / 30
Preliminary Results
0.0
0.2
0.4
0.6
0 500 1000 1500
GDD
T
0.0
0.2
0.4
0.6
0 500 1000 1500
GDD
T
0.0
0.2
0.4
0.6
0 500 1000 1500
GDD
T
0.0
0.2
0.4
0.6
0 500 1000 1500
GDD
T
Figure 3: Pointwise 95% CI bands (for the mean) for pixels 1, 5, 10, and 20 in
2015.
short name May 14, 2018 16 / 30
Preliminary Results
0.0
0.2
0.4
0.6
0.8
0
500
1000
1500
GDD
T
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1000
1500
GDD
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0.0
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0.8
0
500
1000
1500
GDD
T
Figure 4: Median of mixture posterior (red), and 95% CI bands for 3 separate
crops: other (brown), corn (yellow), and soybean (green) for pixels 1, 5, 10, and
20 in 2015.
short name May 14, 2018 17 / 30
1 Introduction: OCO-2 and SMOS data
2 Parametric un-mixing
3 Non-parametric un-mixing
4 Gap-filling Hyperspectral OCO-2 data
short name May 14, 2018 18 / 30
Data Model: Non-parametric approach
For a given curve Ys,k(t),
s = 1, · · · , S: locations, k = 1, · · · , K: years (replicates), t = 1, · · · , T,
and j = 1, · · · , J: mixing components
Ys,k(t) =
J
j=1
πs,k,j
L
l=1
βjlBl(t) +
J
j
s,k,j(t),
where s,k,j(t) ∼ N(0, σ2).
short name May 14, 2018 19 / 30
Likelihood
Y SKT×1
=
(Y11(t1), · · · , Y1K(t1), · · · , Y11(tT ), · · · , Y1K(tT ), · · · , YSK(tT ))T
βJL×1
= (β11, · · · , β1L, β21, · · · , β2L, · · · , βJL)T
XSKT×JL
=


π111B1(t1) · · · π111BL(t1) · · · π11J B1(t1) · · · π11J BL(t
... · · ·
... · · ·
... · · ·
...
πSK1B1(tT ) · · · πSK1BL(tT ) · · · πSKJ B1(tT ) · · · πSKJ BL(t
L(β, σ2; y) ∝ (σ2)−SKT/2 exp{−
1
2σ2
(y − Xβ)T (y − Xβ)}
short name May 14, 2018 20 / 30
Prior & Posterior
β ∼ N(0, τI)
σ2 ∼ IG(a, b)
p(β, σ2; y) ∝ L(β, σ2; y)p(β)p(σ2)
Bayesian regression problem
short name May 14, 2018 21 / 30
SMOS Data
Convert Ys,k(t) to functional data with 8(=L) B-spline basis functions
πsjk are assumed known.
Corn + Soybean =85% and other vegetation=15%
60% corn and 40% soybean for the non ”other’ crops
πs,k,1 = 0.51(Corn)
πs,k,2 = 0.34(Soybean)
πs,k,3 = 0.15(Other) for all s and k.
short name May 14, 2018 22 / 30
Prior Specifiction
There is a gold standard for two curves (corn & soy): Nebraska Data
Convert these data to functional with 8 B-spline basis functions
Compute mean and standard deviation of the estimated coefficients
βjl ∼ N(meanjl, 3 × SDjl)
Without informative prior, the last component (Other) is badly
behaved. Assume that this is a constant
πs,k,j
L
l=1
β3lBl(t) = β0
short name May 14, 2018 23 / 30
Posterior Result
0 50 100 150
0.00.10.20.30.40.5
doy
Tau corn
soy
others
short name May 14, 2018 24 / 30
1 Introduction: OCO-2 and SMOS data
2 Parametric un-mixing
3 Non-parametric un-mixing
4 Gap-filling Hyperspectral OCO-2 data
short name May 14, 2018 25 / 30
Model for OCO-2 data
FPCA
r(wj, si) = f(wj, si) + ij
f(wj, si) = µ(wj) +
∞
k=1
ξk(si)φk(wj)
Assume spatial independence and local stationarity to estimate φk(wj). ij
is assumed to be uncorrelated with mean 0 and variance σ2(g(si)) where
g(si) is a function of location si. First 1, 2, 3 PCs explain 98%, 99.9%,
99.9996% of variation respectively.
Kriging
Model each principle component score ξk(s) (k = 1, 2, · · · , K), as a
stationary random field for spatial prediction.
short name May 14, 2018 26 / 30
Measurement error in OCO-2
It turns out measurement error depends on the sub-track (1-8)
0.0e+00
5.0e+18
1.0e+19
1.5e+19
250 500 750
wavelength
standarderror
pixel
1
2
3
4
5
6
7
8
0.0e+00
5.0e+18
1.0e+19
1.5e+19
0.0e+00 3.0e+19 6.0e+19 9.0e+19 1.2e+20
mean radiance function
standarderror
pixel
1
2
3
4
5
6
7
8
short name May 14, 2018 27 / 30
OCO-2 Gap Filling Using Spatial Functional Kriging
Create artificial gap of up to 12 pixels to see how the methodology
performs on predicting radiance in the gap and compare the prediction
with the observed value. e1 =
1
m
m
j=1
(f(wj, s0) − r(wj, s0))2
r2(wj, s0)
e2 =
1
m
m
j=1
(f(wj, s0) − r(wj, s0))2
(r(wj, s0) − µ(wj))2
.
2 4 6 8 10 12
0.00.10.20.30.40.50.6
number of gaps
e1
2 4 6 8 10 12
0.00.10.20.30.4
number of gaps
e2
It is pretty safe to fill the gap of up to 6 pixels, then the prediction error
starts to pick up.
short name May 14, 2018 28 / 30
Land vs.Water
Radiance on pure land and pure water pixels are different and has linear
relationship:
0e+00 2e+19 4e+19 6e+19 8e+19 1e+20
0.0e+004.0e+198.0e+191.2e+20
land
water
For a mixed pixel si, can assume
r(wj, si) = αfL(wj, si) + (1 − α)fW (wj, si) + ij.
short name May 14, 2018 29 / 30
Future Work
Complet the work of parametric approach for un-mixing of SMOS
data
Further develop the non-parametric approach for un-mixing of SMOS
data, address issues such as identifiability, introduce spatail
dependence, more efficient computation, etc.
Spatial-temporal modeling of Hyperspectral data: non-stationarity,
include information in time, Hyperspectral un-mixing, etc.
short name May 14, 2018 30 / 30

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CLIM: Transition Workshop - Statistical Approaches for Un-Mixing Problem and Application to Satellite Remote Sensing Data - Zhengyuan Zhu, May 14, 2018

  • 1. Statistical Approaches for Un-Mixing Problem and Application to Satellite Remote Sensing Data Zhengyuan Zhu Joint work with Remote Sensing Sptail Y working group May 14, 2018 short name May 14, 2018 1 / 30
  • 2. Spatial Y Working Group Active Members Jenny Brynjarsdottir (Case Western University) Xinyue Chang (Iowa State University) Maggie Johnson (SAMSI, NCSU) Jon Hobbs (JPL) Colin Lewis-Beck (Iowa State University) Anirban Mondal (Case Western University) Joon Jin Song (Baylor University) Zhengyuan Zhu (Iowa State University) short name May 14, 2018 2 / 30
  • 3. 1 Introduction: OCO-2 and SMOS data 2 Parametric un-mixing 3 Non-parametric un-mixing 4 Gap-filling Hyperspectral OCO-2 data short name May 14, 2018 3 / 30
  • 4. Motivation: Improve the retrieval of OCO-2 Data 34.50 34.75 35.00 35.25 24.0 24.1 24.2 longitude latitude short name May 14, 2018 4 / 30
  • 5. OCO-2 Data 0.0e+00 3.0e+19 6.0e+19 9.0e+19 1.2e+20 250 500 750 wavelength meanradiancefunction pixel 1 2 3 4 5 6 7 8 short name May 14, 2018 5 / 30
  • 6. Spatial X vs Spatial Y Spatial X: Model the retrieval variable (X) as spatial process to improve the retrivel. Spatial Y: Develop spatial-temporal functional model for the hyper-spectral reflectance data (Y) to improve retrieval by Gap-filling the missing data, i.e., impute Y and provide uncertainty of the imputation. Smoothing to reduce the noise in Y. Un-mixing the pixel with mixed land cover (i.e., transition between water and land). short name May 14, 2018 6 / 30
  • 7. Focus on Un-mixing problem What is un-mixing? Disregarding atmospheric effects, the signal recorded by the remote sensing instrument at a pixel is typically a mixture of light scattered by substances located in the field of view. Unmixing refers to any process that separates the pixel measurments from an image into a collection of endmembers and a set of fractional abundances. Endmembers: Represent the pure materials present in the image Abundances: Represent the percentage of each endmember that is present in the pixel. The group decided to focus on the un-mixing problem, which will be the focus of this report. At the end we also report some preliminary results on gap-filling for OCO-2. short name May 14, 2018 7 / 30
  • 8. Another (Simpler) Motivating Example: SMOS Data 2011 - 2017 on 30 footprints (45 km diameter) in northwest Iowa Between 75 - 85 % of footprints devoted to annual crops Satellite makes a pass approximately every 12 - 36 hours at the midlatitudes Approximately 60% of each footprint is planted in corn, and 40% soybean 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 short name May 14, 2018 8 / 30
  • 9. SMOS Data Pix 25 2015 Pix 25 2017 Pix 6 2015 Pix 6 2017 M ay 1 June 1 July 1 Aug 1 Sept1 O ct1 N ov 1 M ay 1 June 1 July 1 Aug 1 Sept1 O ct1 N ov 1 0.0 0.2 0.4 0.6 0.0 0.2 0.4 0.6 Month T Figure 1: Two representative SMOS pixels. short name May 14, 2018 9 / 30
  • 10. Motivating Problem Crop-specific peak is of interest in agriculture. SMOS measurements are largely a mixture of corn and soybean signal in Iowa. Can we develop a model to un-mix SMOS satellite signal into two crop types: corn and soybean? Ground based auxiliary data available to inform the signature of each crop type Objective: Reconstruct crop-specific curves using the model and quantify measures of uncertainty for each crop signal short name May 14, 2018 10 / 30
  • 11. Auxiliary Data Field level data based on experiments in Mead, Nebraska. Shape of corn and soybean is based on growing degree days (GDD). Figure 2: Hornbuckle et al. (2016) short name May 14, 2018 11 / 30
  • 12. 1 Introduction: OCO-2 and SMOS data 2 Parametric un-mixing 3 Non-parametric un-mixing 4 Gap-filling Hyperspectral OCO-2 data short name May 14, 2018 12 / 30
  • 13. Data Model: Parametric approach We translate the SMOS time scale to GDD using ground based temperature data and crop planting dates. We model τ as a function of GDD from using an asymmetric Gaussian (AG) function, a frequently used function to model nonlinear vegetation data. fAG θ (d) =    β + (η − β)exp −(d−δ)2 2σ2 1 d ≤ δ β + (η − β)exp −(d−δ)2 2σ2 2 d > δ short name May 14, 2018 13 / 30
  • 14. Unmixing Model The Cropland Data Layer from the NASS provides the proportion of corn and soybean within each region. Let the proportion for the two dominate crops by defined as: πc (corn), πb (soybean). We assume a common intercept (γ) to capture the remaining ground vegetation that is constant over time. Let r = 1 . . . R denote pixel regions, s = 1 . . . S seasons, and d = 1 . . . D denote GDD. For a given curve Xrs(d), xrs(d) = γrs + πcrsfAG θ1 (d) + πbrsfAG θ2 (d) + rs(d) rs(d) ind. ∼ N(0, σrs) short name May 14, 2018 14 / 30
  • 15. Unmixing Model Assuming the curves are exchangeable, and the signatures for corn and soybean are independent, we an model the parameters hierarchically. Let µj = (µηj , µδj , µσ1j, µσ2j) denote the vector of means for the jth mixture component. We will model these parameters as coming from a multivariate normal distribution and work with the transformed vector µθj = (logit(µηj ), log(µδj ), log(µσ1j), log(µσ2j)) θ1rs ind. ∼ N4(µθ1 , Σ1) θ2rs ind. ∼ N4(µθ2 , Σ2) logit(γrs) ind. ∼ N(µγ, τγ) We put informative priors on the parameter vectors based on MLE estimates of the AG parameters derived from the Nebraska field data. short name May 14, 2018 15 / 30
  • 16. Preliminary Results 0.0 0.2 0.4 0.6 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0 500 1000 1500 GDD T Figure 3: Pointwise 95% CI bands (for the mean) for pixels 1, 5, 10, and 20 in 2015. short name May 14, 2018 16 / 30
  • 17. Preliminary Results 0.0 0.2 0.4 0.6 0.8 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0.8 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0.8 0 500 1000 1500 GDD T 0.0 0.2 0.4 0.6 0.8 0 500 1000 1500 GDD T Figure 4: Median of mixture posterior (red), and 95% CI bands for 3 separate crops: other (brown), corn (yellow), and soybean (green) for pixels 1, 5, 10, and 20 in 2015. short name May 14, 2018 17 / 30
  • 18. 1 Introduction: OCO-2 and SMOS data 2 Parametric un-mixing 3 Non-parametric un-mixing 4 Gap-filling Hyperspectral OCO-2 data short name May 14, 2018 18 / 30
  • 19. Data Model: Non-parametric approach For a given curve Ys,k(t), s = 1, · · · , S: locations, k = 1, · · · , K: years (replicates), t = 1, · · · , T, and j = 1, · · · , J: mixing components Ys,k(t) = J j=1 πs,k,j L l=1 βjlBl(t) + J j s,k,j(t), where s,k,j(t) ∼ N(0, σ2). short name May 14, 2018 19 / 30
  • 20. Likelihood Y SKT×1 = (Y11(t1), · · · , Y1K(t1), · · · , Y11(tT ), · · · , Y1K(tT ), · · · , YSK(tT ))T βJL×1 = (β11, · · · , β1L, β21, · · · , β2L, · · · , βJL)T XSKT×JL =   π111B1(t1) · · · π111BL(t1) · · · π11J B1(t1) · · · π11J BL(t ... · · · ... · · · ... · · · ... πSK1B1(tT ) · · · πSK1BL(tT ) · · · πSKJ B1(tT ) · · · πSKJ BL(t L(β, σ2; y) ∝ (σ2)−SKT/2 exp{− 1 2σ2 (y − Xβ)T (y − Xβ)} short name May 14, 2018 20 / 30
  • 21. Prior & Posterior β ∼ N(0, τI) σ2 ∼ IG(a, b) p(β, σ2; y) ∝ L(β, σ2; y)p(β)p(σ2) Bayesian regression problem short name May 14, 2018 21 / 30
  • 22. SMOS Data Convert Ys,k(t) to functional data with 8(=L) B-spline basis functions πsjk are assumed known. Corn + Soybean =85% and other vegetation=15% 60% corn and 40% soybean for the non ”other’ crops πs,k,1 = 0.51(Corn) πs,k,2 = 0.34(Soybean) πs,k,3 = 0.15(Other) for all s and k. short name May 14, 2018 22 / 30
  • 23. Prior Specifiction There is a gold standard for two curves (corn & soy): Nebraska Data Convert these data to functional with 8 B-spline basis functions Compute mean and standard deviation of the estimated coefficients βjl ∼ N(meanjl, 3 × SDjl) Without informative prior, the last component (Other) is badly behaved. Assume that this is a constant πs,k,j L l=1 β3lBl(t) = β0 short name May 14, 2018 23 / 30
  • 24. Posterior Result 0 50 100 150 0.00.10.20.30.40.5 doy Tau corn soy others short name May 14, 2018 24 / 30
  • 25. 1 Introduction: OCO-2 and SMOS data 2 Parametric un-mixing 3 Non-parametric un-mixing 4 Gap-filling Hyperspectral OCO-2 data short name May 14, 2018 25 / 30
  • 26. Model for OCO-2 data FPCA r(wj, si) = f(wj, si) + ij f(wj, si) = µ(wj) + ∞ k=1 ξk(si)φk(wj) Assume spatial independence and local stationarity to estimate φk(wj). ij is assumed to be uncorrelated with mean 0 and variance σ2(g(si)) where g(si) is a function of location si. First 1, 2, 3 PCs explain 98%, 99.9%, 99.9996% of variation respectively. Kriging Model each principle component score ξk(s) (k = 1, 2, · · · , K), as a stationary random field for spatial prediction. short name May 14, 2018 26 / 30
  • 27. Measurement error in OCO-2 It turns out measurement error depends on the sub-track (1-8) 0.0e+00 5.0e+18 1.0e+19 1.5e+19 250 500 750 wavelength standarderror pixel 1 2 3 4 5 6 7 8 0.0e+00 5.0e+18 1.0e+19 1.5e+19 0.0e+00 3.0e+19 6.0e+19 9.0e+19 1.2e+20 mean radiance function standarderror pixel 1 2 3 4 5 6 7 8 short name May 14, 2018 27 / 30
  • 28. OCO-2 Gap Filling Using Spatial Functional Kriging Create artificial gap of up to 12 pixels to see how the methodology performs on predicting radiance in the gap and compare the prediction with the observed value. e1 = 1 m m j=1 (f(wj, s0) − r(wj, s0))2 r2(wj, s0) e2 = 1 m m j=1 (f(wj, s0) − r(wj, s0))2 (r(wj, s0) − µ(wj))2 . 2 4 6 8 10 12 0.00.10.20.30.40.50.6 number of gaps e1 2 4 6 8 10 12 0.00.10.20.30.4 number of gaps e2 It is pretty safe to fill the gap of up to 6 pixels, then the prediction error starts to pick up. short name May 14, 2018 28 / 30
  • 29. Land vs.Water Radiance on pure land and pure water pixels are different and has linear relationship: 0e+00 2e+19 4e+19 6e+19 8e+19 1e+20 0.0e+004.0e+198.0e+191.2e+20 land water For a mixed pixel si, can assume r(wj, si) = αfL(wj, si) + (1 − α)fW (wj, si) + ij. short name May 14, 2018 29 / 30
  • 30. Future Work Complet the work of parametric approach for un-mixing of SMOS data Further develop the non-parametric approach for un-mixing of SMOS data, address issues such as identifiability, introduce spatail dependence, more efficient computation, etc. Spatial-temporal modeling of Hyperspectral data: non-stationarity, include information in time, Hyperspectral un-mixing, etc. short name May 14, 2018 30 / 30