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Landsat properties
History:  Landsat Players - NASA, USGS, USDA Great Sandy Desert, Australia   – NASA Earth Observatory Garden City, Kansas – NASA Earth as Art
Landsat Timeline http://landsat.gsfc.nasa.gov/about/timeline.html
Landsat Sensors and Platforms Chesapeake Bay. Goddard, NASA. http://landsat.gsfc.nasa.gov/news/news-archive/soc_0017.html Platform Sensor Landsat 1 RBV, MSS Landsat 2 RBV, MSS Landsat 3 RBV, MSS Landsat 4 MSS, TM Landsat 5 MSS, TM Landsat 7 ETM+
Return Beam Vidicon (RBV) Three-spectral-band (green, red, near infrared) camera essentially a high-quality, calibrated television camera 2-dimensional array form Considered by some to be unsuccessful
Multispectral Scanner (MSS) Landsats 1-5 (data collected from 1972-1992) Whiskbroom sensor 80m resolution, 185km swath Landsats 1-3: Altitude: 920 km 18 day repeat coverage cycle Landsats 4&5: Altitude: 705km 16 day repeat coverage cycle
UNC. http://www.cpc.unc.edu/projects/nangrong/data/spatial_data/remote_sensing/satellite_imagery/image_inventory/mss_images. EROS, USGS. http://edc.usgs.gov/products/satellite/mss.php Multispectral Scanner (MSS)
Thematic Mapper (TM) Whiskbroom sensor Wavelength range: visible, NIR, MIR, TIR 16 detectors for each visible, NIR, MIR 4 detectors for TIR 30m resolution for visible, NIR, MIR 120m resolution for TIR
Enhanced Thematic Mapper Plus (ETM+) Whiskbroom scanner 183km swath, 705m altitude 16 day repeat cycle 30m 7 bands (RGB, NIR, SWIR1, SWIR2) 15m panchromatic band 60m TIR band EROS, USGS. http://landsat.gsfc.nasa.gov/about/etm+.html
Iraq. Earth Observatory, NASA
Landsat scan line corrector malfunction artifact
 
World Reference System (WRS) Global notation system for Landsat data Each scene center is designated by Path and Row numbers Path: Longitudinal aspect of location; assigned from East to West Row: Latitudinal center line of a frame of imagery WRS-1 used for Landsats 1-3 WRS-2 used for Landsats 4-7 Corrected for differences in repeat cycles, coverage, swath patterns and path/row designators Goddard, NASA. http://landsat.gsfc.nasa.gov/about/wrs.html
 
Radiometric properties Landsats-1, -2 and -3 all carried the Multispectral Scanner (MSS) Radiometric precision of 6 bits (64 possible values) Four spectral bands Landsat-4 and -5 carried Thematic Mapper (TM) Radiometric precision of 8 bits (256 possible values) Seven spectral bands 30 m spatial resolution Radiometric error correction within 1 quantum level Landsat-7 carried Thematic Mapper (TM) Radiometric precision of 8 bits (256 possible values) Bands 1-5 & 7 have 30 m resolution; 6 has 60 m and 8 has 15 m Gain states that allow imaging in low gain states when image is bright; high gain states when image is dark Can set gain for six surface categories (land, desert, ice, water, sea ice, volcano/night)
Sun Elevation and Gain States Source: http://landsathandbook.gsfc.nasa.gov/handbook/handbook_htmls/chapter6/chapter6.html
Data order:  http://glovis.usgs.gov/
Data order:  http://glovis.usgs.gov/
Data information:  http://landsat.usgs.gov/
Data information:  http://landsat.usgs.gov/
Image preprocessing
Cubic Convolution (cont.) Potential use Preferred use on non-categorical data (continuous variables – e.g. temperature, % cover, etc.) Conversion of values during pre-processing stage.
Problem of Varying Illumination USDA Forest Service, Remote Sensing Applications Center,  http://fsweb.rsac.fs.fed.us  and UAS ENVS403
Band B has the Same Problem USDA Forest Service, Remote Sensing Applications Center,  http://fsweb.rsac.fs.fed.us  and UAS ENVS403
Ratio of Band A to Band B USDA Forest Service, Remote Sensing Applications Center,  http://fsweb.rsac.fs.fed.us  and UAS ENVS403
Conversion to reflectance and COST atmospheric correction
Radiance conversion TM Radiance:   Lsat = bias + gain *  DN   ETM+ Radiance: Lsat = ((LMAX λ  - LMIN λ )/(QCALMAX-QCALMIN)) * ( QCAL -QCALMIN) + LMIN λ   Input data are contained in the metadata files of the Landsat TM (gain and bias for each band) or ETM+ (LMAX λ , LMIN λ , QCALMAX,QCALMIN) images Landsat 7 Science Data Users Handbook
 
Reflectance conversion without atmospheric correction ρ  = (PI * L sat λ  * d 2 )/(ESUN λ  * cos θ ) ρ  – planetary reflectance L sat λ   – radiance at sensor d – Earth-Sun distance in astronomical units θ  – solar zenith angle (90 – solar elevation) ESUN λ  mean (by band) solar exoatmospheric irradiance Landsat 7 Science Data Users Handbook
 
Landsat 7 Science Data Users Handbook ETM+ Band ESUN values Band 1 1969 Band 2 1840 Band 3 1551 Band 4 1044 Band 5 225.7 Band 7 82.07
Reflectance conversion + atmospheric correction (COST) REF=   (PI*(Lsat-Lhaze))   (TAUv*(Eo*Cos(TZ)*TAUz+Edown)) Lhaze: upwelling spectral radiance (path radiance),  value derived from image using dark-object criteria;  Calculated by using the dark object criteria (lowest value at the base of the slope of the histogram from either the blue or green band)  TAUv: atmospheric transmittance along the path from ground to sensor,  assumed to be 1 because of nadir look angle Eo: solar spectral irradiance TZ: solar zenith angle, ThetaZ TAUz: atmospheric transmittance along the path from the sun to the ground surface,  =1-TZ 2 /2!+TZ 4 /4!-TZ 6 /6! Edown: downwelling spectral irradiance at the atmosphere Chavez, P.S. Jr (1996). Image-based atmospheric corrections – revisited and improved.  Photogrammetric Engineering and Remote Sensing 62, 1025-1036.
Reflectance conversion + atmospheric correction (COST) Calculate radiance ( L sat)  d = 1 + 0.0167 * sin[2* PI * (JD – 93.5) / 365] L λ 1%  = (0.01 * d2 * cos 2 θ ) / (PI * ESUN λ ) L λ haze  = L λ min  - L λ 1% ρ = (PI * d 2  * (L sat  - L λ haze )) / (ESUN λ  * cos 2 θ ) where JD is the Julian Date (or day of the year , ranges 1- 365), θ is the solar zenith angle (calculated as 90 – solar elevation angle) ESUN – incoming solar radiation by wavelength (see table)
 
Questions?
Spectral Data Transformation for Vegetation Mapping
From Lillesand and Kiefer 1994 Water has a low reflectance because it absorbs EM radiation in the VIS/RIR region Wavelength ( µm) Reflectance (%) Dry bare soil (gray-brown) Vegetation (green) Water (clear) 0.4 0 20 40 60 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 2.2 2.4 2.6
Vegetation and Surface Reflectance Key aspects of reflectance from leaf surfaces Chlorophyll and PAR Water content Leaf structures Multi-layer model of leaf/canopy reflectance Temporal aspects of reflectance from vegetated surfaces
Internal Leaf Structure Chloroplasts Intercellular air labyrinth  CO 2  in & O 2  out
Plant Pigments So, what absorbs EM energy in functioning leaves? (Reflectance   = 100 - Absorption  
Absorption by plant pigments carrying out photosynthesis leads to low plant reflectances in the 0.4 to 0.6    m range
Broadleaf Trees Changing Color Green leaves from a broadleaf tree beginning to change color as nutrients withdraw into the tree core Deciduous broadleaf tree with its colors changed and some leaves fallen on the ground
In situ  Spectra of Fall Leaves Wavelength (µm) Reflectance (%) 0.90 0.60 0.50 0.40 0.30 0.00 0.35 0.60 0.85 1.10 1.35 1.60 1.85 2.35 2.10 0.20 0.10 Fall Leaves 0.80 0.70 2.60 Note reflectance from 0.4 to 0.6   m drops, but 0.6 to 0.7   m increases
Maple & Pine reflectance  maple pine - Pine trees have higher cellulose content than maple trees  - Cellulose absorbs NIR radiation, and lowers reflectance
Trees are complex structures, whose multiple layers of leaves, twigs and branches  Light interacts with individual leaves at a cellular level Light passing through a single leaf then interacts with the next canopy component it encounters
Reflectance from a vegetation canopy decreases as water content increases Water absorbs EM energy in the VIS/RIR region of the EM spectrum    higher water content results in lower reflections
http://research.umbc.edu/~tbenja1/leblon/module9.html See also Figure 10.1 in Jensen
Reflectance curve for a leaf generated from data collected by a spectroradiometer NIR Most digital VIS/IR spaceborne sensors have radiometers with red and near infrared channels Ratios of these two channels are used to create indices of vegetation cover, e.g., vegetation indices
Simple Vegetation Index (VI) VI =  R NIR  / R red Where R IR  is the reflectance in the NIR band R red is the reflectance in the red band
Normalized Difference Vegetation Index NDVI Let R = reflectance in the red channel Let IR = reflectance in the near IR channel IR - R NDVI =  __________ IR + R NDVI ~ amount of green biomass present on the surface
 
 
 
moderate severe
22 band  data set (shown in  7:4:3) Siberia
MSS Component Band 1 Band 2 Band 3 Band 4 Brightness 0.433 0.632 0.586 0.264 Greenness -0.290 -0.562 0.600 0.491 Yellowness -0.829 0.522 -0.039 0.194 "Non-such" 0.223 0.012 -0.543 0.810
TM Component Band 1 Band 2 Band 3 Band 4 Band 5 Band 7 Brightness 0.3037 0.2793 0.4343 0.5585 0.5082 0.1863 Greenness -0.2848 -0.2435 -0.5436 0.7243 0.0840 -0.1800 Wetness 0.1509 0.1793 0.3299 0.3406 -0.7112 -0.4572
Surface reflectance Component Band 1 Band 2 Band 3 Band 4 Band 5 Band 7 Brightness 0.2043 0.4158 0.5524 0.5741 0.3124 0.2303 Greenness -0.1603 -0.2819 -0.4934 0.7940 -0.0002 -0.1446 Wetness 0.0315 0.2021 0.3102 0.1594 -0.6806 -0.6109
Image classification
Image Classification The process of automatically dividing all pixels within a digital remote sensing image into  Land or surface-cover categories Information themes or quantification of specific surface characteristics
Pre-classification masking Masking out selected classes cloud and shadow masks water masks
 
Landsat  Band 4 NIR Water Shadow Cloud
Landsat  Band 4 NIR Shadow Cloud
Masking out water NIR band threshold Manual selection of objects shadow water wetlands dark fields
Final water mask
Supervised versus Unsupervised Classification Supervised classification  – a procedure where the analyst guides or supervises the classification process by specifying numerical descriptors of the land cover types of interest Unsupervised classification  – the computer is allowed to aggregate groups of pixels into like clusters based upon different classification algorithms
Lillesand and Kiefer Figure 7-39
Training Areas and Supervised Classification Specified by the analyst to represent the land cover categories of interest Used to compile a numerical “interpretation key” that describes the spectral attributes of the areas of interest Each pixel in the scene is compared to the training areas, and then assigned to one of the categories
Training area selection: regions of interest
Training area selection: regions of interest
Decision Tree Classifier Decision tree classifiers use a simple set of rules to divide pixels into different land cover types (binary splits along the most lines of greatest separability)
 
 
 
Hybrid Classification Approach Perform an unsupervised classification to create a number of land cover categories within the area of interest Carry out field surveys to identify the land cover type represented by different unsupervised clusters Use a supervised approach to combine unsupervised clusters into similar land cover categories
Sources of Uncertainty in Image Classification Non-representative training areas High variability in the spectral signatures for a land cover class Mixed land cover within the pixel area
Post-classification processing
Additional class detection Land use-based classes Croplands  Manual and automated mix for selection
Removing speckle Using sieving procedure to remove areas less than 5 pixels Reduces data noise Defines a minimum mapping unit
Accuracy Assessment
Accuracy assessment It is necessary to provide information about the accuracy of a giving mapping approach -  different applications require different levels of accuracy
Types of accuracy assessment/ validation Inventory assessment -  e.g. how many acres of forest we get through our classification vs. how many acres of forest is reported by forest service Confusion matrix -  provides information on both – the accuracy of the amount mapped and the accuracy of geographic distribution
Inventory assessment Advantages: -  fairly straightforward method;  -  comparison against ground data. Disadvantages: -  strongly depends on the accuracy of provided information (underreporting, not up-to-date data, etc.) - does not describe spatial accuracy
Confusion Matrix Advantages: -  provides statistics for both inventory and geographic information Disadvantages: -  limited availability of comparable ground truth data (very difficult and expensive to collect, not available in many areas)
Validation sample selection NELDA example: Minimum of 300 randomly selected points across the image with proportional representation of classes (adjusted to 30 min per class) Class Pixels Prop S Sample TNDC 5% 15 30 TNO 7% 21 30 TMC 26% 78 78 TMO 17% 51 51
Confusion matrix NELDA project example for aggregated classes
Confusion matrix NELDA project example for all classes
Statistics Overall accuracy = correct/total in % Full legend accuracy = 541/647 = 0.8362 = 83.62% Kappa value = (Observed agreement - Chance agreement)/(1 - Chance agreement) Observed agreement = (210 + 37) / 252 = 0.98 Chance agreement = (0.845*0.841) + (0.155*0.159) = 0.735 Kappa = (0.98 - 0.735) / (1 – 0.735) = 0.925 Forest Grass Total Forest 210 (83.3%) 3 (1.2%) 213 (84.5%) Grass 2 (0.8%) 37 (14.7%) 39 (15.5%) Total 212 (84.1%) 40 (15.9%) 252
Change Detection
Map overlay problems Involves compiled error from individual datasets – extremely difficult to estimate error propagation
General approaches to change detection Image differencing Select proper dates to account for phenology “ anniversary date images” Well preprocessed input images georegistration within 0.5 pixel image normalization
Change detection of tree dominated landscapes using Disturbance Index Classify “mature forests” in the image Normalize Tasseled Cap Brightness, Greenness, and Wetness by mature forest parameters Br = (B - B µ) / B σ Gr = (G - G µ) / G σ Wr = (W - W µ) / W σ where Br, Br, Wr are rescaled brightness, greenness and wetness,  B µ,  G µ, and  W µ - mean values for “mature forest” and B σ , G σ , W σ  are standard deviation of the respective parameters for “mature forest” S.P. Healey, W.B. Cohen, Y. Zhiqiang, O. Krankina. 2005. Comparison of Tasseled Cap-Based Landsat Data Structures for Use in Forest Disturbance Detection. Remote Sensing of Environment 97: 301 – 310.
Change detection of tree dominated landscapes using Disturbance Index DI = Br – (Gr + Wr) Change detection: DI date1  – DI date2 Multi-date classification (maximum likelihood) S.P. Healey, W.B. Cohen, Y. Zhiqiang, O. Krankina. 2005. Comparison of Tasseled Cap-Based Landsat Data Structures for Use in Forest Disturbance Detection. Remote Sensing of Environment 97: 301 – 310.
NELDA project example
Emerging new methods (trajectory analysis) Huang, C., Goward, S.N., Schleeweis, K., Thomas, N., Masek, J.G., & Zhu, Z. (2009) Dynamics of National Forests Assessed Using the Landsat Record: Case Studies in Eastern U.S.  Remote Sensing of Environment. 113(7) : 1430-1442.
 
 
 
 
 
Accuracy assessment: random pixel selection Randomly distributed 300 points 150 points for “unchanged” and 150 points for “changed” forests Within the categories validation pixels were distributed proportionally by the total number of pixels within the category Analyst visually assigned the validation pixels to specific categories Accuracy assessment was performed using the confusion matrix and Kappa values
Summer Cottage Development
Forest Harvest
NELDA example: Change detection random sample accuracy assessment
Accuracy assessment: analyst driven validation sample selection Analyst visually selected a higher number of validation pixels per class from the images Accuracy assessment was performed using the confusion matrix and Kappa values
NELDA example: Change detection analyst driven accuracy assessment
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Lecture for landsat

  • 2. History: Landsat Players - NASA, USGS, USDA Great Sandy Desert, Australia – NASA Earth Observatory Garden City, Kansas – NASA Earth as Art
  • 4. Landsat Sensors and Platforms Chesapeake Bay. Goddard, NASA. http://landsat.gsfc.nasa.gov/news/news-archive/soc_0017.html Platform Sensor Landsat 1 RBV, MSS Landsat 2 RBV, MSS Landsat 3 RBV, MSS Landsat 4 MSS, TM Landsat 5 MSS, TM Landsat 7 ETM+
  • 5. Return Beam Vidicon (RBV) Three-spectral-band (green, red, near infrared) camera essentially a high-quality, calibrated television camera 2-dimensional array form Considered by some to be unsuccessful
  • 6. Multispectral Scanner (MSS) Landsats 1-5 (data collected from 1972-1992) Whiskbroom sensor 80m resolution, 185km swath Landsats 1-3: Altitude: 920 km 18 day repeat coverage cycle Landsats 4&5: Altitude: 705km 16 day repeat coverage cycle
  • 7. UNC. http://www.cpc.unc.edu/projects/nangrong/data/spatial_data/remote_sensing/satellite_imagery/image_inventory/mss_images. EROS, USGS. http://edc.usgs.gov/products/satellite/mss.php Multispectral Scanner (MSS)
  • 8. Thematic Mapper (TM) Whiskbroom sensor Wavelength range: visible, NIR, MIR, TIR 16 detectors for each visible, NIR, MIR 4 detectors for TIR 30m resolution for visible, NIR, MIR 120m resolution for TIR
  • 9. Enhanced Thematic Mapper Plus (ETM+) Whiskbroom scanner 183km swath, 705m altitude 16 day repeat cycle 30m 7 bands (RGB, NIR, SWIR1, SWIR2) 15m panchromatic band 60m TIR band EROS, USGS. http://landsat.gsfc.nasa.gov/about/etm+.html
  • 11. Landsat scan line corrector malfunction artifact
  • 12.  
  • 13. World Reference System (WRS) Global notation system for Landsat data Each scene center is designated by Path and Row numbers Path: Longitudinal aspect of location; assigned from East to West Row: Latitudinal center line of a frame of imagery WRS-1 used for Landsats 1-3 WRS-2 used for Landsats 4-7 Corrected for differences in repeat cycles, coverage, swath patterns and path/row designators Goddard, NASA. http://landsat.gsfc.nasa.gov/about/wrs.html
  • 14.  
  • 15. Radiometric properties Landsats-1, -2 and -3 all carried the Multispectral Scanner (MSS) Radiometric precision of 6 bits (64 possible values) Four spectral bands Landsat-4 and -5 carried Thematic Mapper (TM) Radiometric precision of 8 bits (256 possible values) Seven spectral bands 30 m spatial resolution Radiometric error correction within 1 quantum level Landsat-7 carried Thematic Mapper (TM) Radiometric precision of 8 bits (256 possible values) Bands 1-5 & 7 have 30 m resolution; 6 has 60 m and 8 has 15 m Gain states that allow imaging in low gain states when image is bright; high gain states when image is dark Can set gain for six surface categories (land, desert, ice, water, sea ice, volcano/night)
  • 16. Sun Elevation and Gain States Source: http://landsathandbook.gsfc.nasa.gov/handbook/handbook_htmls/chapter6/chapter6.html
  • 17. Data order: http://glovis.usgs.gov/
  • 18. Data order: http://glovis.usgs.gov/
  • 19. Data information: http://landsat.usgs.gov/
  • 20. Data information: http://landsat.usgs.gov/
  • 22. Cubic Convolution (cont.) Potential use Preferred use on non-categorical data (continuous variables – e.g. temperature, % cover, etc.) Conversion of values during pre-processing stage.
  • 23. Problem of Varying Illumination USDA Forest Service, Remote Sensing Applications Center, http://fsweb.rsac.fs.fed.us and UAS ENVS403
  • 24. Band B has the Same Problem USDA Forest Service, Remote Sensing Applications Center, http://fsweb.rsac.fs.fed.us and UAS ENVS403
  • 25. Ratio of Band A to Band B USDA Forest Service, Remote Sensing Applications Center, http://fsweb.rsac.fs.fed.us and UAS ENVS403
  • 26. Conversion to reflectance and COST atmospheric correction
  • 27. Radiance conversion TM Radiance: Lsat = bias + gain * DN ETM+ Radiance: Lsat = ((LMAX λ - LMIN λ )/(QCALMAX-QCALMIN)) * ( QCAL -QCALMIN) + LMIN λ Input data are contained in the metadata files of the Landsat TM (gain and bias for each band) or ETM+ (LMAX λ , LMIN λ , QCALMAX,QCALMIN) images Landsat 7 Science Data Users Handbook
  • 28.  
  • 29. Reflectance conversion without atmospheric correction ρ = (PI * L sat λ * d 2 )/(ESUN λ * cos θ ) ρ – planetary reflectance L sat λ – radiance at sensor d – Earth-Sun distance in astronomical units θ – solar zenith angle (90 – solar elevation) ESUN λ mean (by band) solar exoatmospheric irradiance Landsat 7 Science Data Users Handbook
  • 30.  
  • 31. Landsat 7 Science Data Users Handbook ETM+ Band ESUN values Band 1 1969 Band 2 1840 Band 3 1551 Band 4 1044 Band 5 225.7 Band 7 82.07
  • 32. Reflectance conversion + atmospheric correction (COST) REF= (PI*(Lsat-Lhaze)) (TAUv*(Eo*Cos(TZ)*TAUz+Edown)) Lhaze: upwelling spectral radiance (path radiance), value derived from image using dark-object criteria; Calculated by using the dark object criteria (lowest value at the base of the slope of the histogram from either the blue or green band) TAUv: atmospheric transmittance along the path from ground to sensor, assumed to be 1 because of nadir look angle Eo: solar spectral irradiance TZ: solar zenith angle, ThetaZ TAUz: atmospheric transmittance along the path from the sun to the ground surface, =1-TZ 2 /2!+TZ 4 /4!-TZ 6 /6! Edown: downwelling spectral irradiance at the atmosphere Chavez, P.S. Jr (1996). Image-based atmospheric corrections – revisited and improved. Photogrammetric Engineering and Remote Sensing 62, 1025-1036.
  • 33. Reflectance conversion + atmospheric correction (COST) Calculate radiance ( L sat) d = 1 + 0.0167 * sin[2* PI * (JD – 93.5) / 365] L λ 1% = (0.01 * d2 * cos 2 θ ) / (PI * ESUN λ ) L λ haze = L λ min - L λ 1% ρ = (PI * d 2 * (L sat - L λ haze )) / (ESUN λ * cos 2 θ ) where JD is the Julian Date (or day of the year , ranges 1- 365), θ is the solar zenith angle (calculated as 90 – solar elevation angle) ESUN – incoming solar radiation by wavelength (see table)
  • 34.  
  • 36. Spectral Data Transformation for Vegetation Mapping
  • 37. From Lillesand and Kiefer 1994 Water has a low reflectance because it absorbs EM radiation in the VIS/RIR region Wavelength ( µm) Reflectance (%) Dry bare soil (gray-brown) Vegetation (green) Water (clear) 0.4 0 20 40 60 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 2.2 2.4 2.6
  • 38. Vegetation and Surface Reflectance Key aspects of reflectance from leaf surfaces Chlorophyll and PAR Water content Leaf structures Multi-layer model of leaf/canopy reflectance Temporal aspects of reflectance from vegetated surfaces
  • 39. Internal Leaf Structure Chloroplasts Intercellular air labyrinth CO 2 in & O 2 out
  • 40. Plant Pigments So, what absorbs EM energy in functioning leaves? (Reflectance  = 100 - Absorption  
  • 41. Absorption by plant pigments carrying out photosynthesis leads to low plant reflectances in the 0.4 to 0.6  m range
  • 42. Broadleaf Trees Changing Color Green leaves from a broadleaf tree beginning to change color as nutrients withdraw into the tree core Deciduous broadleaf tree with its colors changed and some leaves fallen on the ground
  • 43. In situ Spectra of Fall Leaves Wavelength (µm) Reflectance (%) 0.90 0.60 0.50 0.40 0.30 0.00 0.35 0.60 0.85 1.10 1.35 1.60 1.85 2.35 2.10 0.20 0.10 Fall Leaves 0.80 0.70 2.60 Note reflectance from 0.4 to 0.6  m drops, but 0.6 to 0.7  m increases
  • 44. Maple & Pine reflectance  maple pine - Pine trees have higher cellulose content than maple trees - Cellulose absorbs NIR radiation, and lowers reflectance
  • 45. Trees are complex structures, whose multiple layers of leaves, twigs and branches Light interacts with individual leaves at a cellular level Light passing through a single leaf then interacts with the next canopy component it encounters
  • 46. Reflectance from a vegetation canopy decreases as water content increases Water absorbs EM energy in the VIS/RIR region of the EM spectrum  higher water content results in lower reflections
  • 48. Reflectance curve for a leaf generated from data collected by a spectroradiometer NIR Most digital VIS/IR spaceborne sensors have radiometers with red and near infrared channels Ratios of these two channels are used to create indices of vegetation cover, e.g., vegetation indices
  • 49. Simple Vegetation Index (VI) VI = R NIR / R red Where R IR is the reflectance in the NIR band R red is the reflectance in the red band
  • 50. Normalized Difference Vegetation Index NDVI Let R = reflectance in the red channel Let IR = reflectance in the near IR channel IR - R NDVI = __________ IR + R NDVI ~ amount of green biomass present on the surface
  • 51.  
  • 52.  
  • 53.  
  • 55. 22 band data set (shown in 7:4:3) Siberia
  • 56. MSS Component Band 1 Band 2 Band 3 Band 4 Brightness 0.433 0.632 0.586 0.264 Greenness -0.290 -0.562 0.600 0.491 Yellowness -0.829 0.522 -0.039 0.194 "Non-such" 0.223 0.012 -0.543 0.810
  • 57. TM Component Band 1 Band 2 Band 3 Band 4 Band 5 Band 7 Brightness 0.3037 0.2793 0.4343 0.5585 0.5082 0.1863 Greenness -0.2848 -0.2435 -0.5436 0.7243 0.0840 -0.1800 Wetness 0.1509 0.1793 0.3299 0.3406 -0.7112 -0.4572
  • 58. Surface reflectance Component Band 1 Band 2 Band 3 Band 4 Band 5 Band 7 Brightness 0.2043 0.4158 0.5524 0.5741 0.3124 0.2303 Greenness -0.1603 -0.2819 -0.4934 0.7940 -0.0002 -0.1446 Wetness 0.0315 0.2021 0.3102 0.1594 -0.6806 -0.6109
  • 60. Image Classification The process of automatically dividing all pixels within a digital remote sensing image into Land or surface-cover categories Information themes or quantification of specific surface characteristics
  • 61. Pre-classification masking Masking out selected classes cloud and shadow masks water masks
  • 62.  
  • 63. Landsat Band 4 NIR Water Shadow Cloud
  • 64. Landsat Band 4 NIR Shadow Cloud
  • 65. Masking out water NIR band threshold Manual selection of objects shadow water wetlands dark fields
  • 67. Supervised versus Unsupervised Classification Supervised classification – a procedure where the analyst guides or supervises the classification process by specifying numerical descriptors of the land cover types of interest Unsupervised classification – the computer is allowed to aggregate groups of pixels into like clusters based upon different classification algorithms
  • 68. Lillesand and Kiefer Figure 7-39
  • 69. Training Areas and Supervised Classification Specified by the analyst to represent the land cover categories of interest Used to compile a numerical “interpretation key” that describes the spectral attributes of the areas of interest Each pixel in the scene is compared to the training areas, and then assigned to one of the categories
  • 70. Training area selection: regions of interest
  • 71. Training area selection: regions of interest
  • 72. Decision Tree Classifier Decision tree classifiers use a simple set of rules to divide pixels into different land cover types (binary splits along the most lines of greatest separability)
  • 73.  
  • 74.  
  • 75.  
  • 76. Hybrid Classification Approach Perform an unsupervised classification to create a number of land cover categories within the area of interest Carry out field surveys to identify the land cover type represented by different unsupervised clusters Use a supervised approach to combine unsupervised clusters into similar land cover categories
  • 77. Sources of Uncertainty in Image Classification Non-representative training areas High variability in the spectral signatures for a land cover class Mixed land cover within the pixel area
  • 79. Additional class detection Land use-based classes Croplands Manual and automated mix for selection
  • 80. Removing speckle Using sieving procedure to remove areas less than 5 pixels Reduces data noise Defines a minimum mapping unit
  • 82. Accuracy assessment It is necessary to provide information about the accuracy of a giving mapping approach - different applications require different levels of accuracy
  • 83. Types of accuracy assessment/ validation Inventory assessment - e.g. how many acres of forest we get through our classification vs. how many acres of forest is reported by forest service Confusion matrix - provides information on both – the accuracy of the amount mapped and the accuracy of geographic distribution
  • 84. Inventory assessment Advantages: - fairly straightforward method; - comparison against ground data. Disadvantages: - strongly depends on the accuracy of provided information (underreporting, not up-to-date data, etc.) - does not describe spatial accuracy
  • 85. Confusion Matrix Advantages: - provides statistics for both inventory and geographic information Disadvantages: - limited availability of comparable ground truth data (very difficult and expensive to collect, not available in many areas)
  • 86. Validation sample selection NELDA example: Minimum of 300 randomly selected points across the image with proportional representation of classes (adjusted to 30 min per class) Class Pixels Prop S Sample TNDC 5% 15 30 TNO 7% 21 30 TMC 26% 78 78 TMO 17% 51 51
  • 87. Confusion matrix NELDA project example for aggregated classes
  • 88. Confusion matrix NELDA project example for all classes
  • 89. Statistics Overall accuracy = correct/total in % Full legend accuracy = 541/647 = 0.8362 = 83.62% Kappa value = (Observed agreement - Chance agreement)/(1 - Chance agreement) Observed agreement = (210 + 37) / 252 = 0.98 Chance agreement = (0.845*0.841) + (0.155*0.159) = 0.735 Kappa = (0.98 - 0.735) / (1 – 0.735) = 0.925 Forest Grass Total Forest 210 (83.3%) 3 (1.2%) 213 (84.5%) Grass 2 (0.8%) 37 (14.7%) 39 (15.5%) Total 212 (84.1%) 40 (15.9%) 252
  • 91. Map overlay problems Involves compiled error from individual datasets – extremely difficult to estimate error propagation
  • 92. General approaches to change detection Image differencing Select proper dates to account for phenology “ anniversary date images” Well preprocessed input images georegistration within 0.5 pixel image normalization
  • 93. Change detection of tree dominated landscapes using Disturbance Index Classify “mature forests” in the image Normalize Tasseled Cap Brightness, Greenness, and Wetness by mature forest parameters Br = (B - B µ) / B σ Gr = (G - G µ) / G σ Wr = (W - W µ) / W σ where Br, Br, Wr are rescaled brightness, greenness and wetness, B µ, G µ, and W µ - mean values for “mature forest” and B σ , G σ , W σ are standard deviation of the respective parameters for “mature forest” S.P. Healey, W.B. Cohen, Y. Zhiqiang, O. Krankina. 2005. Comparison of Tasseled Cap-Based Landsat Data Structures for Use in Forest Disturbance Detection. Remote Sensing of Environment 97: 301 – 310.
  • 94. Change detection of tree dominated landscapes using Disturbance Index DI = Br – (Gr + Wr) Change detection: DI date1 – DI date2 Multi-date classification (maximum likelihood) S.P. Healey, W.B. Cohen, Y. Zhiqiang, O. Krankina. 2005. Comparison of Tasseled Cap-Based Landsat Data Structures for Use in Forest Disturbance Detection. Remote Sensing of Environment 97: 301 – 310.
  • 96. Emerging new methods (trajectory analysis) Huang, C., Goward, S.N., Schleeweis, K., Thomas, N., Masek, J.G., & Zhu, Z. (2009) Dynamics of National Forests Assessed Using the Landsat Record: Case Studies in Eastern U.S. Remote Sensing of Environment. 113(7) : 1430-1442.
  • 97.  
  • 98.  
  • 99.  
  • 100.  
  • 101.  
  • 102. Accuracy assessment: random pixel selection Randomly distributed 300 points 150 points for “unchanged” and 150 points for “changed” forests Within the categories validation pixels were distributed proportionally by the total number of pixels within the category Analyst visually assigned the validation pixels to specific categories Accuracy assessment was performed using the confusion matrix and Kappa values
  • 105. NELDA example: Change detection random sample accuracy assessment
  • 106. Accuracy assessment: analyst driven validation sample selection Analyst visually selected a higher number of validation pixels per class from the images Accuracy assessment was performed using the confusion matrix and Kappa values
  • 107. NELDA example: Change detection analyst driven accuracy assessment

Editor's Notes

  • #3: Landsat was conceived by a NASA study group in 1967, inspired by the Gemini and Apollo space missions. 3 p517 USGS and the USDA were also interested in helping shape the design of the Landsat system. 3 p517 http://earthobservatory.nasa.gov/Newsroom/NewImages/images.php3?img_id=10815 http://earthasart.gsfc.nasa.gov/garden.html
  • #4: The first Landsat was launched in 1972, and from 1972 to 1982, the Landsat mission was sustained as a NASA experimental activity. The Landsat 7 mission Terrestrial research and applications for the 21st century In 1982, began a period of commercial and operational missions, before returning to government management in 1992, with both experimental and operational activities.
  • #6: The RBV system on Landsats 1 and 2 consisted of three television-like cameras aimed to view the same 185 km-by-185 km area as the multispectral scanner (MSS) sensor. The RBV system did not contain film. The images were exposed by a shutter device and stored on a photosensitive surface within each camera. This surface is then scanned in raster form by an internal electron beam to produce a video signal. The RBV system instantaneously imaged an entire scene, had greater inherent cartographic fidelity than imagery acquired by the Landsat MSS sensor, and contained a reseau grid in the image to facilitate geometric correction of the imagery. This resulted in an array of tick marks that were precisely placed in each image. The RBV system on Landsat 1 produced only 1690 scenes between July 23 and August 5, 1972, when a tape recording switching problem forced a system shutdown. The RBV system on Landsat 2 was operated primarily for engineering evaluation purposes and only occasional RBV imagery was obtained, primarily for cartographic uses in remote areas. These images are no longer available.
  • #7: Landsats 1 through 3 operated in a near-polar orbit at an altitude of 920 km with an 18-day repeat coverage cycle. These satellites circled the Earth every 103 minutes, completing 14 orbits a day. Eighteen days and 251 overlapping orbits were required to provide nearly complete coverage of the Earth's surface with 185 km wide image swaths. The amount of swath overlap or sidelap varies from 14 percent at the Equator to a maximum of approximately 85 percent at 81 degrees north or south latitude. Landsat satellites 1 through 3 carried return beam vidicon (RBV) cameras and the MSS sensor. The RBV cameras did not achieve the popularity of the MSS sensor. The MSS sensor scanned the Earth's surface from west to east as the satellite moved in its descending (north-to-south) orbit over the sunlit side of the Earth. Six detectors for each spectral band provided six scan lines on each active scan. The combination of scanning geometry, satellite orbit, and Earth rotation produced the global coverage necessary for studying land surface change. The resolution of the MSS sensor was approximately 80 m with radiometric coverage in four spectral bands from the visible green to the near-infrared (IR) wavelengths. Only the MSS sensor on Landsat 3 had a fifth band in the thermal-IR wavelength. Landsats 4 and 5 carried both the MSS and the TM sensors; however, routine collection of MSS data was terminated in late 1992. The satellites orbited at an altitude of 705 km and provide a 16-day, 233-orbit cycle with a swath overlap that varies from 7 percent at the Equator to nearly 84 percent at 81 degrees north or south latitude. These satellites were also designed and operated to collect data over a 185 km swath. The MSS sensors flown aboard Landsats 4 and 5 were identical to the ones that were carried on Landsats 1 and 2.
  • #9: The MSS and TM sensors primarily detected reflected radiation from the Earth's surface in the visible and IR wavelengths, but the TM sensor provides more radiometric information than the MSS sensor. The wavelength range for the TM sensor is from the visible (blue), through the mid-IR, into the thermal-IR portion of the electromagnetic spectrum. Sixteen detectors for the visible and mid-IR wavelength bands in the TM sensor provide 16 scan lines on each active scan. Four detectors for the thermal-IR band provide four scan lines on each active scan. The TM sensor has a spatial resolution of 30 meters for the visible, near-IR, and mid-IR wavelengths and a spatial resolution of 120 meters for the thermal-IR band. Freden, S.C. & Gorden, F., Jr. (1983). Landsat Satellites. In Manual of Remote Sensing (ed R.N. Colwell), Vol. 1, pp. 517-570. American Society of Photogrammetry, Falls Church, Virginia . Sun-synchronous, repetitive orbit of 16 days with an equatorial altitude of 703km, a 9:45am local sun time overpass, and a 30x30m IFOV. p548-9 233 orbits per cycle. p565 To get the necessary signal strength so that an acceptable signal-to-noise detector performance can be achieved, the sweep rate of the scanning mirror had to be slowed down from 13.67 cycles per second to 6.999 cycles per second. Also, it scans in both directions – west to east and east to west. Landsats 1-5 have been in Sun-synchronous orbits with equatorial crossing times ranging from 8:30 a.m. for Landsat 1 to approximately 9:45 a.m. for Landsat 5. A Landsat-4 or -5 TM scene has an instantaneous field of view (IFOV) of 30 meters by 30 meters (900 square meters) in bands 1 through 5 and band 7, and an IFOV of 120 meters by 120 meters (14,400 square meters) on the ground in band 6.
  • #10: The Enhanced Thematic Mapper Plus (ETM+) instrument is a fixed "whisk-broom", eight-band, multispectral scanning radiometer capable of providing high-resolution imaging information of the Earth's surface. It detects spectrally-filtered radiation in VNIR, SWIR, LWIR and panchromatic bands from the sun-lit Earth in a 183 km wide swath when orbiting at an altitude of 705 km. The primary new features on Landsat 7 are a panchromatic band with 15 m spatial resolution, an on-board full aperture solar calibrator, 5% absolute radiometric calibration and a thermal IR channel with a four-fold improvement in spatial resolution over TM. Landsat 7 collects data in accordance with the World Wide Reference System 2, which has catalogued the world's land mass into 57,784 scenes, each 183 km wide by 170 km long. The ETM+ produces approximately 3.8 gigabits of data for each scene. An ETM+ scene has an Instantaneous Field Of View (IFOV) of 30 meters in bands 1-5 and 7 while band 6 has an IFOV of 60 meters on the ground and the band 8 an IFOV of 15 meters. Please visit the L7 Science Data Users Handbook for a detailed description of ETM+ spatial characteristics . GSFC, NASA
  • #14: The Worldwide Reference System (WRS) is a global notation system for Landsat data. It enables a user to inquire about satellite imagery over any portion of the world by specifying a nominal scene center designated by PATH and ROW numbers. The WRS has proven valuable for the cataloging, referencing, and day-to-day use of imagery transmitted from the Landsat sensors.
  • #38: Broad categories of surfaces have very different reflections as seen on this plot These differences are very obvious when one looks at the reflectance curves from three different surface Here we have reflectance curves from 3 common surfaces Soil – Generally has high reflectance which increases gradually, but stays fairly constant in the IR Water – very low reflectance in all  regions Vegetation –complex, low in some, high in others - low less than .6 um, high in near IR, and then drops in Middle IR The differences in reflectance provide the basis for discrimination between these surfaces For example, what would it take for us to tell the difference between these three surfaces – could probably easily do it with two channels, say one at 0.5 um, and a second at 1.0 Make chart of differences in reflectance on board in two wavelength regions
  • #40: IF you were actually an EM wavelength of light going into a leaf, this is what you would see at the molecular level You have a bunch of cells, that have intercellular air spaces, and a bunch of chloroplast cells that absorb visible light
  • #41: Going back to basic biology, it is a set of plant pigments in the chloroplasts that absorb EM radiation – These pigments are converting EM radiation into sugars through the process of photosynthesis There are several different plant pigments, each that absorb EM radiation in different wavelength regions
  • #43: We all know that the color of leaves change in the fall This is because chlorophyll begins to die, and therefore the reflectance of the leaf changes
  • #45: Two plant or tree types might have very similar levels of chlorophyll and moisture, but still have different reflectances The microscopic structure of foliage can influence absorption and scattering, and hence influence reflection For example, needles are much different than leaves, they have much higher levels of cellulose that absorbs EM energy, especially Near IR EM energy Hence pine trees have different spectral signatures than deciduous trees, as seen in this graph
  • #46: GO OUTSIDE AND LOOK AT A TREE When you are talking about reflectance of vegetation, you have to realize that we are dealing with a process that occurs at microscopic levels Therefore, you really have to look at reflectance at the cellular structure of the leaf that is doing the reflecting There are three major components of the leaf that influence reflection Chlorophyll Water content IF you take these two away, then you are dealing with the cellular structure of the leaf itself, e.g., the leaf structures that comprise the leaf Next, you need to realize that a single leaf not only reflects energy, but it absorbs and transmits energy Thus, you really have to think of a vegetation canopy as a multiple layer of different surfaces that reflect, absorb, and transmit energy Also, this leaves on vegetation change throughout time A very complex surface
  • #47: Transition to next plot Here we have the same tree species that was monitored under different leaf moisture conditions Note that there are distinct variations in the spectral reflectance as a function of leaf moisture Reflectance from vegetated surface is a complex process What I want to do is to discuss the sources of variations in plant reflectance GO TO NEXT SLIDE
  • #48: Here is one way to view the three processes controlling reflection from a plant surface Leaf pigments dominate reflectance in the visible Cell structure dominates in the near IR Water absorption dominates in the shortwave IR
  • #52: Different forest types will have different seasonal profiles because they have different levels of green biomass present For example, we see that black and white spruce forests, which have lower reflectance in the Near IR, also have lower NDVI signatures during the summer time In this case, you can use the seasonal profile of NDVI to discriminate between spruce and aspen forests
  • #53: You can also use seasonal NDVI profiles to analyze differences in vegetation condition between years In this case, we see that NDVI in 1992 was lower than in 1991 Note the green up in the spring of 1992 was later 1992 had a late spring, and overall cooler temperatures because of the eruption of Mount Pinatubo
  • #54: First example is our study region in Alaska
  • #55: Our field studies and analysis of landsat imagery showed that the heavy burned area had a higher reflectance in bands 4 (IR) and 7 (SWIR) than the light burned areas This is because of two things Mineral soil versus organic soil (organic soil has lower reflectance) No shadows in severe burned resulted in higher radiance We were able to use the spectral information in a supervised classification approach to map burn severity
  • #61: Image Classification – it is a very broad area of research in remote sensing Perhaps one of the most intensive areas of research in the field over the past 30 years In this lecture, I want to briefly review some of the basic approaches to image classification – because in many cases, what you are going to see is an image product that is based on a classification approach
  • #68: Supervised classification typically uses something called training sets or areas WRITE ON BOARD Training areas Specified by the analyst to represent the land cover categories of interest Used to compile a numerical “interpretation key” that describes the spectral attributes of the areas of interest Each pixel in the scene is compared to the training sets, and then assigned to one of the categories
  • #73: Most land cover products from AVHRR time series data are derived using decision tree classifiers