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to determine land cover and a subsequent change detection. The data were field
validated to produce a land cover inventory for Massachusetts. If you wish to
create an attribute table to identify the different land cover change
classifications, an easy reference table is available under the PROCESS
DESCRIPTION section.</gco:CharacterString>
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            <gco:CharacterString>To improve the understanding of coastal uplands and wetlands, and
their linkages with the distribution, abundance, and health of living marine
resources.

SPATIAL DATA ORGANIZATION INFORMATION 
Direct Spatial Reference: Raster

SPATIAL REFERENCE INFORMATION - PLANAR 
Grid Coordinate System Name: Universal Transverse Mercator
UTM Zone Number: 19
Scale Factor at Central Meridian: 1
Longitude of Central Meridian: -69
Latitude of Projection Origin: 0
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False Northing: 0.00000
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Ordinate Resolution: 30
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SPATIAL REFERENCE INFORMATION - GEODETIC MODEL 
Horizontal Datum Name: North American Datum 1983
Ellipsoid Name: GRS80
Semi-major Axis: 6378206.4
Denominator of Flattening Ratio: 294.98

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      ACCESS CONSTRAINTS: None, except for a possible fee at the cost of
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      DISTRIBUTION LIABILITY: Users must assume responsibility to determine the
      usability of these data. 
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      Data set is not for use in litigation. While efforts have been made to ensure
      that these data are accurate and reliable within the state of the art, NOAA,
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      ATTRIBUTE ACCURACY REPORT: A team of field investigators participated in data
      verification exercises on December 1999 , September 2000. Data validation teams
      consisted of personnel from the NOAA Coastal Services Center and Oak Ridge
      National Laboratory. Each team was equipped with a portable color laptop
      computer linked to a Global Positioning System (GPS). The field station runs
      software that supports the classified data as a raster background with the road
      network as a vector overlay with a simultaneous display of live GPS
      coordinates. Accuracy assessment points were generated with ERDAS Imagine
      software using a stratified random sample in 3x3 pixel homogeneous windows. To
      make the acquisition of the field reference data more practical, a twenty pixel
      buffer area around roads (i.e. 10 pixels on each side of the road) was created.
      7,000 random points were generated within this area for the accuracy
      assessment. 376 of these points were verified for accuracy assessment purposes.
      Collection of ground reference information for areas that have experienced a
      change in land cover type is a troublesome task. Pre-Processing Steps: The
      scene was georectified to UTM Zone 19 coordinates. Ancillary data sets:
      Subsequent field work and the use of collateral data such as USGS maps, county
      marsh inventories, and National Wetland Inventory data led to further
      refinements in the image classification. Shoreline features can be extracted
      from Landsat images by detecting the land/water interface. However, care must
      be used to avoid misinterpreting tidal differences as changes in shorelines,
      since the satellite images from which these land cover images are derived and
      acquired at different tidal stages, depending on when the satellite is
      overhead. The land cover classifications represent the instantaneous state of
      the shoreline at the moment of image acquisition. C-CAP data are mapped at
      1:100,000 scale with 22 standard classes constituting major landscape
      components. They are not jurisdictional (can't be used for permitting) and will
      not identify individual species. However, they are useful for identifying
      regional landscape patterns, major functional niches, environmental impact
      assessment, urban planning, and zoning applications. If you need change
      analysis data at this scale, C-CAP may be your only option. C-CAP is designed
      around a 1 to 5 year revisit cycle. Land Cover is the complete human and
      natural landscape recorded as surface components - forest, water, wetlands,
      concrete, asphalt, etc. Land cover can be documented by analyzing spectral
      signatures of satellite and aerial imagery. Land Use is the documentation of
      human uses of the landscape - residential, commercial, agricultural, etc. Land
      use can be inferred but, not explicitly derived from satellite and aerial
      imagery. There is no spectral basis for land use determination in satellite
      imagery. C-CAP data can be used to identify concrete and asphalt as land cover,
      but we can only infer that these materials denote a residential or commercial
      use. Post-Processing Steps: None Known Problems: Due to shadows and cumulus
      cloud coverage portions of the 1997 image sections were unclassified. Therefore
      pieces of Path and Row 12/31 19980610 were used to rectify the image
      classification. Accuracy Results: This data set was found to be 86.7% accurate
      with a Kappa coefficient of 0.848. 
      
      LOGICAL CONSISTENCY REPORT: Tests for logical consistency indicate that all row
      and column positions in the selected latitude/longitude window contain data.
      Conversion and integration with vector files indicates that all positions are
      consistent with earth coordinates covering the same area. Attribute files
      appear to be logically consistent. Examining the change matrix for logical
      fallacies, we find, for example, that a very small number of pixels changed
      from developed land to any other category. 
      
      COMPLETENESS REPORT: The classification scheme comprehensively includes all
      anticipated land covers, and all pixels have been classified. The NOAA Coastal
      Change Analysis Program (C-CAP): Guidance for Regional Implementation, NOAA
      National Marine Fisheries Service Report 123, discusses the interagency effort
      to develop the land cover classification scheme and defines all categories. 
      
      HORIZONTAL POSITIONAL ACCURACY REPORT: Precision corrected images were
      purchased from the EROS Data Center in UTM NAD27 meters to an RMSE +/- 0.5
      pixels. 
      
      VERTICAL POSITIONAL ACCURACY REPORT: There was no terrain correction in the
      georeferencing procedure. 
      
      PROCESS DESCRIPTION: The processing steps for each C-CAP Massachusetts 1991 -
      1997 Land Cover Change Analysis product are intricately associated. Each
      database is the result of many processing steps with numerous iterations for
      each step. The output of one processing step or database is often the input
      data for another processing step. A brief description of the processing steps
      used in the land cover classification of the this project follows. Further
      description of the processing steps can be found in the NOAA Coastal Change
      Analysis Program (C-CAP): Guidance for Regional Implementation, NOAA National
      Marine Fisheries Service Report 123 (Dobson et al, 1995). Baseline
      Classification Process: The Massachusetts land cover/change classification
      product was processed using an iterative classification approach. Landsat
      Thematic Mapper data for path/row/date(s): 12/31 19910607, 12/31 19970623,
      12/31 19980610 were analyzed to create a land cover for the Massachusetts. Each
      scene was classified, focusing first on separating major categories (e.g.
      water, forest, marsh, herbaceous upland, and developed) using standard
      supervised classification techniques. Numerous individual areas were chosen as
      training sites for the land cover classification. The mean and covariance
      statistics for these areas are passed to an isodata classification algorithm
      which assigns an unknown pixel to the class in which it has the highest
      probability of being a member. Then iterative unsupervised classifications were
      performed on each major category individually by masking out all other major
      categories. With this type of unsupervised classification, the computer is
      allowed to query the multispectral properties of the masked scene using user
      specified criteria and to identify X mutually exclusive clusters in
      N-dimensional feature space. By masking out all data but a single major
      category, the spectral variance is greatly reduced thus decreasing
      classification errors. After several classification iterations of the masked
      data, final classification labels were assigned to the spectral clusters.
      Changes among major categories were permitted to occur even at this stage of
      processing. Subsequent field work and the use of collateral data such as USGS
      maps, TIGER road data, and National Wetland Inventory data led to further
      refinements in the image classification. In small areas where landcover class
      confusion could not be separated spectrally, human pattern recognition was used
      to recode the data. A spatial filter was applied to the final classification
      data file. Change Classification Process: Landsat Thematic Mapper data for
      path/row(s) 12/31 19910607, 12/31 19970623, 12/31 19980610 were analyzed to
      arrive at a land cover for Massachusetts. The change date land cover
      classification was in part derived from the baseline classification. Only the
      pixels in the June 23, 1997 image that changed spectrally from the change date
      image were classified for the June 7, 1991 data file. All other pixels were
      simply replaced with the baseline image classification. It is possible to
      simply identify the amount of change between two images by image differencing
      the same band in two images which have previously been rectified to a common
      basemap. Image differencing involves subtracting the imagery of one date from
      that of another. The subtraction results in positive and negative values in
      areas of radiance change and zero values in areas of no-change in a new 'change
      image'. The images are subtracted resulting in an signed 16-bit analysis with
      pixel values ranging from -255 to 255. The results were transformed into
      positive unsigned 16-bit values by adding a constant, c. The operation is
      expressed mathematically as: Dijk = BVijk(1) - BVijk(2) + c where Dijk = change
      pixel value BVijk(1) = brightness value at time 1 BVijk(2) = brightness value
      at time 2 c = a constant (e.g., 255). i = line number j = column number k = a
      single band (e.g. TM band 4). The 'change image' produced using image
      differencing usually yields a BV distribution approximately gaussian in nature,
      where pixels of no BV change are distributed around the mean and pixels of
      change are found in the tails of the distribution. A threshold value was
      carefully chosen to identify spectral 'change' and 'no-change' pixels in the
      'change image.' A 'change/no-change' mask was derived by performing image
      differencing on band 4, and Normalized Difference Vegetation Index (NDVI) of
      the two date dataset and recoded into a binary mask file. The
      'change/no-change' mask was then overlaid onto the earlier date of imagery and
      only those pixels which were detected as having spectrally changed were viewed
      as candidate pixels for categorical change. Change Detection Database The
      change date and baseline land cover classifications were compared on a pixel by
      pixel basis using a change detection matrix. This traditional
      post-classification comparison yields 'from land cover class - to land cover
      class' change information. Many pixels with sufficient change to be included in
      the mask of candidate pixels in the spectral change process did not qualify as
      categorical land cover change. This method may reduce change detection errors
      (omission and commission) and provides detailed 'from-to' change class
      information. The technique reduces effort by allowing analysts to focus on the
      small amount of area that has changed between dates. PROCESS DATE: 20010120
      
      PROCESS DESCRIPTION: This data was projected to Universal Transverse Mercator
      zone 19 with a horizontal datum of NAD83. PROCESS DATE: Unknown
      
      SOURCE INFORMATION - CITATION: Earth Observation Satellite Company. Landsat
      Thematic Mapper Source_Geospatial_Data_Presentation_Form: remote-sensing image.
      1997-06-23. OTHER CITATION DETAILS: Landsat Thematic Mapper scenes processed:
      Path = 12 Row = 31 Date 06-10-1998 Path = 12 Row = 31 Date 06-23-1997 Path = 12
      Row = 31 Date 06-07-1991 
      TYPE OF SOURCE MEDIA: CD-ROM. 
      SOURCE CURRENTNESS REFERENCE: ground condition. 
      SOURCE CITATION ABBREVIATION: Massachusetts_91/97_LTMi. 
      SOURCE CONTRIBUTION: Source used in land cover classification.
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