Title pseudo-hyperspectral image synthesi. Author(s) Hoang, Nguyen Tien; Koike, Katsuaki.

Similar documents
Basic Hyperspectral Analysis Tutorial

ENVI Tutorial: Hyperspectral Signatures and Spectral Resolution

The studies began when the Tiros satellites (1960) provided man s first synoptic view of the Earth s weather systems.

APPLICATION OF HYPERSPECTRAL REMOTE SENSING IN TARGET DETECTION AND MAPPING USING FIELDSPEC ASD IN UDAYGIRI (M.P.)

Textbook, Chapter 15 Textbook, Chapter 10 (only 10.6)

IKONOS High Resolution Multispectral Scanner Sensor Characteristics

Hyperspectral image processing and analysis

NON-PHOTOGRAPHIC SYSTEMS: Multispectral Scanners Medium and coarse resolution sensor comparisons: Landsat, SPOT, AVHRR and MODIS

Introduction of Satellite Remote Sensing

Hyperspectral Image Data

STRIPING NOISE REMOVAL OF IMAGES ACQUIRED BY CBERS 2 CCD CAMERA SENSOR

University of Texas at San Antonio EES 5053 Term Project CORRELATION BETWEEN NDVI AND SURFACE TEMPERATURES USING LANDSAT ETM + IMAGERY NEWFEL MAZARI

1. Theory of remote sensing and spectrum

Application of Satellite Image Processing to Earth Resistivity Map

Remote Sensing of the Environment An Earth Resource Perspective John R. Jensen Second Edition

IEEE GEOSCIENCE AND REMOTE SENSING LETTERS, VOL. 3, NO. 1, JANUARY Chein-I Chang, Senior Member, IEEE, and Antonio Plaza, Member, IEEE

An Introduction to Remote Sensing & GIS. Introduction

HYPERSPECTRAL IMAGERY FOR SAFEGUARDS APPLICATIONS. International Atomic Energy Agency, Vienna, Austria

Geology, Exploration, and WorldView-3 SWIR Kumar Navulur, PhD

Bisun Datt, Tim R. McVicar, Tom G. Van Niel, David L. B. Jupp, Associate Member, IEEE, and Jay S. Pearlman, Senior Member, IEEE

Comprehensive Application on Extraction of Mineral Alteration and Mapping from ETM+ Sensors and ASTER Sensors Data in Ethiopia

Spotlight on Hyperspectral

Geometric Validation of Hyperion Data at Coleambally Irrigation Area

Satellite Remote Sensing: Earth System Observations

REMOTE SENSING. Topic 10 Fundamentals of Digital Multispectral Remote Sensing MULTISPECTRAL SCANNERS MULTISPECTRAL SCANNERS

PLEASE SCROLL DOWN FOR ARTICLE

MOVING FROM PIXELS TO PRODUCTS

746A27 Remote Sensing and GIS. Multi spectral, thermal and hyper spectral sensing and usage

Evaluation of Sentinel-2 bands over the spectrum

Evaluation of FLAASH atmospheric correction. Note. Note no SAMBA/10/12. Authors. Øystein Rudjord and Øivind Due Trier

NEC s EO Sensors and Data Applications

Sommersemester Prof. Dr. Christoph Kleinn Institut für Waldinventur und Waldwachstum Arbeitsbereich Fernerkundung und Waldinventur.

Leaf Area Index Estimation Using MESMA Based on EO-1 Hyperion Satellite Imagery

Hyperspectral Remote Sensing

The studies began when the Tiros satellites (1960) provided man s first synoptic view of the Earth s weather systems.

Super-Resolution of Multispectral Images

MULTISPECTRAL IMAGE PROCESSING I

Application of GIS to Fast Track Planning and Monitoring of Development Agenda

Using Freely Available. Remote Sensing to Create a More Powerful GIS

TEMPORAL ANALYSIS OF MULTI EPOCH LANDSAT GEOCOVER IMAGES IN ZONGULDAK TESTFIELD

INTERNATIONAL JOURNAL OF PURE AND APPLIED RESEARCH IN ENGINEERING AND TECHNOLOGY

An Introduction to Geomatics. Prepared by: Dr. Maher A. El-Hallaq خاص بطلبة مساق مقدمة في علم. Associate Professor of Surveying IUG

Lecture 6: Multispectral Earth Resource Satellites. The University at Albany Fall 2018 Geography and Planning

Solid Earth Timeline with a smattering of cryosphere technology

International Journal of Engineering Research & Science (IJOER) ISSN: [ ] [Vol-2, Issue-2, February- 2016]

remote sensing? What are the remote sensing principles behind these Definition

REVIEW OF ENMAP SCIENTIFIC POTENTIAL AND PREPARATION PHASE

SEA GRASS MAPPING FROM SATELLITE DATA

Some Basic Concepts of Remote Sensing. Lecture 2 August 31, 2005


NORMALIZING ASTER DATA USING MODIS PRODUCTS FOR LAND COVER CLASSIFICATION

Hyperspectral Imagery: A New Tool For Wetlands Monitoring/Analyses

Ground Truth for Calibrating Optical Imagery to Reflectance

LANDSAT 8 Level 1 Product Performance

Remote Sensing Platforms

Texture characterization in DIRSIG

CHAPTER 7: Multispectral Remote Sensing

Remote Sensing. The following figure is grey scale display of SPOT Panchromatic without stretching.

typical spectral signatures of photosynthetically active and non-photosynthetically active vegetation (Beeri et al., 2007)

Spectral Signatures. Vegetation. 40 Soil. Water WAVELENGTH (microns)

PRELIMINARY EXPERIMENT OF SIMPLE FIELD SPECTROSCOPY BY USING FILTERED COMMERCIAL DIGITAL CAMERA

Mapping Open Water Bodies with Optical Remote Sensing

Sensor resolutions from space: the tension between temporal, spectral, spatial and swath. David Bruce UniSA and ISU

EnMAP Environmental Mapping and Analysis Program

IDENTIFICATION AND MAPPING OF HAWAIIAN CORAL REEFS USING HYPERSPECTRAL REMOTE SENSING

Mod. 2 p. 1. Prof. Dr. Christoph Kleinn Institut für Waldinventur und Waldwachstum Arbeitsbereich Fernerkundung und Waldinventur

Comparative Study of MLH and SAM Classification Techniques using Multispectral Data of EO-1 Satellite

Kelp Canopy Biomass, Landsat 5 TM. Santa Barbara Coastal LTER (2011, 2013)

9/12/2011. Training Course Remote Sensing Basic Theory & Image Processing Methods September 2011

Advanced satellite image fusion techniques for estimating high resolution Land Surface Temperature time series

The Evolution of Spectral Remote Sensing from Color Images to Imaging Spectroscopy

Introduction to Remote Sensing

MRLC 2001 IMAGE PREPROCESSING PROCEDURE

ENVI Classic Tutorial: Spectral Angle Mapper (SAM) and Spectral Information Divergence (SID) Classification 2

Int n r t o r d o u d c u ti t on o n to t o Remote Sensing

Airborne hyperspectral data over Chikusei

Monitoring agricultural plantations with remote sensing imagery

FLIGHT SUMMARY REPORT

APCAS/10/21 April 2010 ASIA AND PACIFIC COMMISSION ON AGRICULTURAL STATISTICS TWENTY-THIRD SESSION. Siem Reap, Cambodia, April 2010

Lesson 3: Working with Landsat Data

Using IRS Products to Recover 7ETM + Defective Images

Preparing Remote Sensing Data for Natural Resources Mapping (image enhancement, rectifications )

DESIS Applications & Processing Extracted from Teledyne & DLR Presentations to JACIE April 14, Ray Perkins, Teledyne Brown Engineering

Module 3 Introduction to GIS. Lecture 8 GIS data acquisition

ENVI Tutorial: Advanced Hyperspectral Analysis

Remote Sensing Mapping of Turbidity in the Upper San Francisco Estuary. Francine Mejia, Geography 342

Update on Landsat Program and Landsat Data Continuity Mission

Statistical Analysis of SPOT HRV/PA Data

DISTINGUISHING URBAN BUILT-UP AND BARE SOIL FEATURES FROM LANDSAT 8 OLI IMAGERY USING DIFFERENT DEVELOPED BAND INDICES

29 th Annual Louisiana RS/GIS Workshop April 23, 2013 Cajundome Convention Center Lafayette, Louisiana

MULTI-SENSOR DATA FUSION OF VNIR AND TIR SATELLITE IMAGERY

746A27 Remote Sensing and GIS

How to Access Imagery and Carry Out Remote Sensing Analysis Using Landsat Data in a Browser

PLANET SURFACE REFLECTANCE PRODUCT

Coral Reef Remote Sensing

Abstract Quickbird Vs Aerial photos in identifying man-made objects

A broad survey of remote sensing applications for many environmental disciplines

On the use of water color missions for lakes in 2021

3/31/03. ESM 266: Introduction 1. Observations from space. Remote Sensing: The Major Source for Large-Scale Environmental Information

Relationship Between Landsat 8 Spectral Reflectance and Chlorophyll-a in Grand Lake, Oklahoma

Transcription:

Title Hyperspectral transformation from E pseudo-hyperspectral image synthesi Author(s) Hoang, Nguyen Tien; Koike, Katsuaki International Archives of the Photo Citation and Spatial Information Sciences - XLI-B7: 661-665 Issue Date 2016-06-21 URL http://hdl.handle.net/2433/217225 RightPublished under the Creative Common Type Journal Article Textversion publisher Kyoto University

HYPERSPECTRAL TRANSFORMATION FROM EO-1 ALI IMAGERY USING PSEUDO-HYPERSPECTRAL IMAGE SYNTHESIS ALGORITHM Nguyen Tien Hoang a,b, Katsuaki Koike a, a Graduate School of Engineering, Kyoto University, Katsura C1-2-215, Kyoto 615-8540, Japan - koike.katsuaki.5x@kyoto-u.ac.jp b Department of Environmental Science, College of Sciences, Hue University, 77 Nguyen Hue, Hue, Vietnam - nguyenhoanggis@gmail.com Commission VII, WG VII/6 KEY WORDS: Hyperspectral data, multiple analysis, spectral reconstruction, Hyperion, ALI ABSTRACT: Hyperspectral remote sensing is more effective than multispectral remote sensing in many application fields because of having hundreds of observation bands with high spectral resolution. However, hyperspectral remote sensing resources are limited both in temporal and spatial coverage. Therefore, simulation of hyperspectral imagery from multispectral imagery with a small number of bands must be one of innovative topics. Based on this background, we have recently developed a method, Pseudo-Hyperspectral Image Synthesis Algorithm (PHISA), to transform Landsat imagery into hyperspectral imagery using the correlation of reflectance at the corresponding bands between Landsat and EO-1 Hyperion data. This study extends PHISA to simulate pseudo-hyperspectral imagery from EO-1 ALI imagery. The pseudo-hyperspectral imagery has the same number of bands as that of high-quality Hyperion bands and the same swath width as ALI scene. The hyperspectral reflectance data simulated from the ALI data show stronger correlation with the original Hyperion data than the one simulated from Landsat data. This high correlation originates from the concurrent observation by the ALI and Hyperion sensors that are on-board the same satellite. The accuracy of simulation results are verified by a statistical analysis and a surface mineral mapping. With a combination of the advantages of both ALI and Hyperion image types, the pseudo-hyperspectral imagery is proved to be useful for detailed identification of minerals for the areas outside the Hyperion coverage. 1. INTRODUCTION Recent advances in hyperspectral remote sensing (also known as imaging spectroscopy) have demonstrated that hyperspectral imagery is more effective than multispectral imagery in many application fields because of having hundreds of observation bands with high spectral resolution. However, hyperspectral remote sensing resources are limited both in temporal and spatial coverage. Therefore, simulation of hyperspectral imagery from multispectral imagery with a small number of bands must be one of innovative topics. The National Aeronautics and Space Administration EO-1 satellite was successfully launched on November 21, 2000. EO-1 brings three sensors including the multispectral Advanced Land Imager (ALI), the hyperspectral Hyperion sensor, and the Linear Etalon Imaging Spectrometer Array (LEISA) Atmospheric Corrector (LAC). EO-1 Hyperion, a representative space-based imaging spectroscopy, enables a wide range of applications, including mining, geology, forestry, agriculture and environmental management. Hyperion covers the - 2.5 µm wavelength range with 242 bands at approximately 10 nm spectral resolution and 30 m spatial resolution. Despite this spectral superiority, its image scene is narrower than ALI image scene (Table 1). In addition, ALI data are much less noise than Hyperion data. If ALI imagery can be successfully transformed into Hyperion data, this pseudohyperspectral imagery must be more helpful because of a combination of the advantages of both image types. Since 2008 some researchers have addressed the simulation of Hyperion data from ALI images. Chen et al. (2008) used a model of spectrum mixing based on spectral library and Liu et al. (2009) used the universal pattern decomposition method (UPDM) to acquire simulated hyperspectral images. Both their studies have only focused on ac- Corresponding author quiring pseudo-hyperspectral images inside the area covered by original hyperspectral image scenes. We have recently developed a new method, Pseudo Hyperspectral Image Synthesis Algorithm (PHISA), to transform Landsat ETM+ imagery into hyperspectral imagery using the correlation of reflectance at the corresponding bands between ETM+ and Hyperion data (Hoang and Koike, 2015). This study extends PHISA to simulate the pseudo-hyperspectral imagery from EO-1 ALI imagery. The pseudo-hyperspectral imagery can have the number of bands with the same number as high-quality Hyperion bands and with the same swath width as ALI scene. 2. DATA AND STUDY AREA We used three cloud-free images acquired on 23 July 2001, EO-1 ALI, EO-1 Hyperion and Landsat 7 ETM+ images, which were obtained from USGS Earth Explorer. Figure 1 illustrates the overlap in surface area coverage of the ALI and Hyperion scenes, compared to the Landsat 7 ETM+ ground track. EO-1 flies approximately one minutes behind Landsat 7 with the same sunsynchronous orbit at an altitude of 705 km. Because PHISA was originally developed for Landsat data, the ETM+ imagery was Parameters ALI EO1-Hyperion Spectral range - 2.4 µm - 2.5 µm Spectral resolution Variable 10 nm Spectral coverage Discrete Continuous Number of bands 10 220 Swath width 37 km 7.5 km Spatial resolution 30 m, PAN: 10 m 30 m Temporal resolution Variable Variable Table 1: ALI and Hyperion technical specifications doi:10.5194/isprsarchives-xli-b7-661-2016 661

Landsat 7 ETM+ (185 km) ALI Image: A Hyperion Image: H Pre-processing Pre-processing Cuprite Geometric intersection data for i = 1,,155 Hyperion (7.5 km) ALI (37 km) Variable selection (BMA) Figure 1: Locations of EO1-Hyperion, ALI and Landsat 7 ETM+ scenes used in this study Best model of all pixels for Band i Band Wavelength (µm) Description PAN 8-9 Panchromatic MS-1 33-53 VNIR (blue) MS-1 5-0.515 VNIR (blue) MS-2 0.525-05 VNIR (green) MS-3 3-9 VNIR (red) MS-4 0.775-0.805 VNIR MS-4 0.845-0.890 VNIR MS-5 1.2-1.3 SWIR MS-5 1.55-1.75 SWIR MS-7 2.08-2.35 SWIR Table 2: Spectral characteristics for the ALI bands Model Dictionary Data Simulation Pseudo-hyperspectral Imagery Figure 2: Flow chart of the PHISA method used to simulate the pseudo-hyperspectral data for comparison with the one simulated from ALI. The spectral characteristics of ALI bands are summarized in Table 2. In the VNIR and SWIR spectral ranges, ALI image consists 9 multispectral bands versus 6 bands of ETM+ image (except for the panchromatic band). All images are cloud-free and located in an area lying on the border of California and Nevada in US (path 41 and row 34). The ALI scene covers the Cuprite alteration zones while the Hyperion scene does not cover this area. Therefore, Cuprite was chosen for validation of the pseudo-hyperspectral data outside the Hyperion scene. With an extremely arid climate condition, the Cuprite site is barren and sparsely vegetated land, which is suitable for remote sensing-based mineral mapping. Cuprite served as the test site of many remote sensing instruments including airborne and orbital visible, near-infrared, thermal-infrared, and hyperspectral sensors (Swayze et al., 2014). To further evaluate PHISA, we selected the AVIRIS image as a ground truth data collected on July 12, 2002 for mineral mapping. The AVIRIS data having a spatial resolution of 15.7 meters was provided in an orthocorrected radiance data format by Jet Propulsion Laboratory. The mineral map for the Cuprite site built from the pseudohyperspectral data was validated by a map classified from the AVIRIS data. 3.1 PHISA 3. METHODS Every reflectance spectra of surface materials usually follow certain rules or behaviours in which a reflectance value at a channel can be predicted from reflectance values of key channels. Based on this idea, PHISA has been developed by assuming that multiple linear regression models can be hold between each of Hyperion bands and Landsat ETM+ bands, in which each Hyperion band is a response variable and Landsat bands are predictor variables (Hoang and Koike, 2015). In this study, we used ALI bands as substitutes of Landsat bands, and then the general form of the multiple linear regression is defined as H ij = β 0i + β 1i.A 1j + β 2i.A 2j + β 3i.A 3j + β 4i.A 4j + β 5i. A 5j + β 6i.A 6j + β 7i.A 7j + β 8i.A 8j + β 9i.A 9j + ε ij, (1) where H ij represents pixel value of Hyperion image at band i and location j; β 0i is intercept at Hyperion band i; β 1i, β 2i, β 3i, β 4i, β 5i, β 6i, β 7i, β 8i, and β 9i are unknown regression coefficients between ALI bands and Hyperion band i; A 1j, A 2j, A 3j, A 4j, A 5j, A 6j, A 7j, A 8j, and A 9j represent pixel values at location j doi:10.5194/isprsarchives-xli-b7-661-2016 662

A B 0.950 0.950 0.925 0.925 PCC 0.900 0.900 PCC Data 0.875 ALI ETM+ 0.875 0.850 500 1000 1500 2000 Wavelength (nm) 0.850 Figure 3: (A) Comparison between two cases of the pseudo-hyperspectral data simulated from ALI and Landsat ETM+ images for PCCs of the original Hyperion data and the pseudo-hyperspectral data; (B) Boxplot of PCCs between the original Hyperion data and the ALI based pseudo-hyperspectral data for 155 simulated bands Hyperion data suffer from systematic and random noise which was reduced prior to further processing. Accordingly, the Hyperion image was corrected at first for smile effects by the moving linear fitting and interpolation method (Goodenough et al., 2003), and then, for vertical strips at outlier pixels by the local de-striping method (Datt et al., 2003). The ENVI MODTRANbased Fast Line-of-sight Atmospheric Analysis of Spectral Hypercubes (FLAASH) module was used for atmospheric correction and producing surface reflectance images from both ALI and Hyperion data. The C-correction method, a non-lambertian technique, was chosen for topographic correction. Hyperion scene was co-registered to ALI scene. Only the overlapped area of ALI and Hyperion data were used to build the model dictionary. 3.2 Validation Figure 4: Histogram of multiple R-squared R The quality of the pseudo-hyperspectral data are verified by statistical analysis and an application of mineral mapping. Two statistical metrics used in the validation are Pearson s correlation coefficient (PCC) and the root mean square error (RMSE) between the original Hyperion data and the pseudo-hyperspectral data. For mineral mapping, a hyperspectral data analysis approach implemented in the ENVI software, Spectral Hourglass Wizard, was used for both pseudo-hyperspectral and AVIRIS data. The details of this technique are described in Kruse et al. (2003). of ALI Band 1, 1, 2, 3, 4, 4, 5, 5, and 7, respectively; and ε ij is random error (residual) at band i and location j. Bayesian model averaging (BMA) method is applied to correctly determine the relevant ALI bands in every Hyperion band regenerating models. The variable selection was done using BMA package in R programming language. The best model, which was selected from a set of possible models, has the lowest Bayesian Information Criterion (BIC) and the highest posterior probability (Raftery et al., 2005). This model is used to build the corresponding pseudo-hyperspectral band which has the same swath width as the ALI scene. Flow chart of the PHISA method is shown in Figure 2. 4.1 Statistical analysis 4. RESULTS AND DISCUSSION The accuracy of each multiple linear regression model between Hyperion and ALI bands was confirmed by a high coefficient of determination (multiple R-squared). Most models had the multiple R-squared higher than 90% (Figure 4). The highest, mean and lowest values are 92.7%, 9% and 74.8%, respectively. Some models include all multispectral bands of ALI imagery but some have only 6 bands as predictor variables. Band 2 of ALI imagery appears the most frequently (155 times), while Band 4 is less frequently observed (128 times) in the models. However, we are of the opinion that these frequencies may be changed according to study area because types and area ratios of surface materials are different. Since all multiple linear regression models achieved high accuracies, ALI imagery was transformed into 155 bands of the pseudohyperspectral imagery. The most remarkable result to emerge doi:10.5194/isprsarchives-xli-b7-661-2016 663

The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XLI-B7, 2016 117o12'30''W Band 185 37o34'N A 37o32'N Reflectance of pseudo data R2 = 0.75 n = 1,308,006 0 Reflectance of original data 1 km Band 157 37o34'N R2 = 0.93 Alunite Kaolinite Muscovite Hydrated silica Buddingtonite N B 37o32'N Reflectance of pseudo data 117o10'W n = 1,308,006 Reflectance of original data 1 km Figure 5: Examples of linear regression between the original Hyperion data and the pseudo-hyperspectral data at Bands 157 and 185 from the statistical analysis is that most bands have PCCs > 0.95. Only a small fraction of pseudo-bands has the coefficients < 0.93 like outliers in the dataset (Figure 3B). Even the lowest correlation coefficient was still high at 0.86. In addition, the RMSE values, which are consistent with PCCs, are mainly low, smaller than 0.016. Figure 3A shows plots of PCCs between the original Hyperion data and the pseudo-hyperspectral data for two cases of the pseudo-hyperspectral data simulated from ALI and Landsat ETM+ images. It is noteworthy that the curve of ALI based pseudo-data is above that of the Landsat based pseudodata, which means the pseudo-hyperspectral data simulated from the ALI data is more strongly correlated with the original Hyperion data than the one simulated from Landsat data. This high correlation originates from the concurrent observation by the ALI and Hyperion sensors that are on-board the same satellite. The results revealed consistent agreements between the original 117o12'30''W 117o10'W Figure 6: Mineral maps of spectrally dominant selected endmembers for the pseudo-hyperspectral data (A) and AVIRIS (B). Background is grayscale of the pseudo-hyperspectral band 190 Hyperion data and the pseudo-hyperspectral data, with correlation slopes close to one (Figure 5). Each coefficient of determination was calculated by using all pixel values of the corresponding band. The highest linearity (R2 = 0.93) that was identified in the case of Band 157 confirmed the strong similarity of the pseudo-data to the original data for this band. Even the lowest coefficient of determination was still high in the case of Band 185 (R2 = 0.75). Those observations suggest the statistical suitability of PHISA for transforming ALI imagery into the pseudohyperspectral imagery. 4.2 Mineral mapping Spectral bands covering the SWIR ranges (2.0-2.4 µm) of the pseudo-hyperspectral and AVIRIS data were selected for mineral mapping. The pseudo-data was co-registered and resampled to AVIRIS data. Five basic mineral endmembers, which consists of doi:10.5194/isprsarchives-xli-b7-661-2016 664

AVIRIS Ground Truth (%) Pseudo-data endmembers Alunite Kaolinite Muscovite Buddingtonite Hydrated silica Alunite 89.40 81.35 0.08 0.00 0.00 Kaolinite 9.54 16.84 0.00 0.00 0.00 Muscovite 0.00 0.06 99.92 0.00 0.00 Buddingtonite 1.03 1.75 0.00 100.00 0.00 Hydrated silica 0.03 0.00 0.00 0.00 100.00 Table 3: Confusion matrix comparing the mineral mapping results between pseudo-hyperspectral and AVIRIS images kaolinite, alunite, muscovite, hydrated silica (chalcedony and/or opal), and buddingtonite, were determined based on the result of purest pixels in n-dimensional space (n-d Visualizer). Spectral Angle Mapper (SAM) method was used to produce distribution and abundance maps of selected minerals. One ALI band in the 2.2 µm region was transformed into 37 bands of the pseudo-hyperspectral data. This result is very important to identify mineralogical composition by exploiting absorptions found in the SWIR region. The mineral maps show both satisfactory and unexpected results (Figure 6). Muscovite and hydrated silica were well identified from the pseudo-data while most pixels classified by AVIRIS as kaolinite were misclassified as alunite on the pseudo-data. It is interesting to note that buddingtonite that isolated into small areas can be extracted from the pseudo-data. The confusion matrix revealed that there were two high classification errors in alunite mapped by the pseudo-data as kaolinite (9.54%) and kaolinite mapped by the pseudo-data as alunite (81.35%) (Table 3). Despite the fact that the classification accuracy of muscovite, hydrated silica, and buddingtonite were 99.9%, 100%, and 100%, respectively, the kaolinite classification error declined the overall agreement of the pseudo-data with AVIRIS fall to 63%. This requires further improvements of PHISA to separate endmembers having similar reflectance spectra. 5. CONCLUSIONS Datt, B., McVicar, T., Van Niel, T., Jupp, D. and Pearlman, J., 2003. Preprocessing EO-1 Hyperion hyperspectral data to support the application of agricultural indexes. IEEE Transactions on Geoscience and Remote Sensing, 41(6), pp. 1246-1259. Goodenough, D. G., Dyk, A., Niemann, K. O., Pearlman, J. S., Chen, H., Han, T., Murdoch, M. and West, C., 2003. Processing Hyperion and ALI for forest classification. IEEE Transactions on Geoscience and Remote Sensing, 41(6), pp. 1321-1331. Hoang, N. T. and Koike, K., 2015. Development of Bayesianbased transformation method of Landsat imagery into pseudohyperspectral imagery. In: Proc. SPIE 9643, Image and Signal Processing for Remote Sensing XXI, 96430J, pp. 96430J-1-96430J-6. Kruse, F. A., Boardman, J. W. and Huntington, J. F., 2003. Comparison of Airborne Hyperspectral Data and EO-1 Hyperion for Mineral Mapping. IEEE Transactions on Geoscience and Remote Sensing, 41(6), pp. 1388-1400. Liu, B., Zhang, L., Zhang, X., Zhang, B. and Tong, Q., 2009. Simulation of EO-1 Hyperion Data from ALI Multispectral Data Based on the Spectral Reconstruction Approach. Sensors, 9(4), pp. 3090-3108. Raftery, A. E., Painter, I. S. and Volinsky, C. T., 2005. BMA: An R package for Bayesian Model Averaging. R News, 5(2), pp. 2-8. We applied PHISA to transform EO-1 ALI imagery into 155 bands of the pseudo-hyperspectral imagery and produced the pseudodata with the same swath width as ALI scene. Most pseudo-bands have PCCs bigger than 0.95 and RMSE values smaller than 0.016. The strong similarities between each band data of Hyperion and the pseudo-hyperspectral reflectances have further strengthened our confidence in extending applications of PHISA. Despite the statistical suitability and very high classification accuracy of muscovite, hydrated silica, and buddingtonite, the mineral mapping result showed that kaolinite were mostly misclassified as alunite. Future work should concentrate on improving PHISA by assigning the best model to each surface pattern over all bands. We believe that the improvement can reduce the unexpected performance by separating endmembers having similar reflectance spectra. Swayze, G. A., Clark, R. N., Goetz, A. F. H., Livo, K. E., Breit, G. N., Kruse, F. A., Sutley, S. J., Snee, L. W., Lowers, H. A., Post, J. L., Stoffregen, R. E. and Ashley, R. P., 2014. Mapping Advanced Argillic Alteration at Cuprite, Nevada, Using Imaging Spectroscopy. Economic Geology, 109(5), pp. 1179-1221. ACKNOWLEDGEMENTS We are grateful to USGS and NASA for providing us with raw EO-1 Hyperion, ALI, Landsat 7 ETM+ and AVIRIS images. REFERENCES Chen, F., Niu, Z., Sun, G., Wang, C. and Teng, J., 2008. Using low-spectral-resolution images to acquire simulated hyperspectral images. International Journal of Remote Sensing, 29(10), pp. 2963-2980. doi:10.5194/isprsarchives-xli-b7-661-2016 665