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                  <gco:CharacterString>Entity and Attribute Overview: For easier readability, this XML metadata can be opened in a text editor (e.g., Notepad). The Paterson, NJ Meter-Scale Urban Land Cover (MULC) dataset was developed using five United States Department of Agriculture (USDA) National Agriculture Imagery Program (NAIP) Digital Orthophoto Quarter Quadrangles (DOQQ) ("quarter quads"). Each quarter quad is 4 bands including visible RGB and a Near Infrared (NIR) band with 1 meter pixel resolution. All quarter quads were projected in NAD83/UTM 18N. Supervised classifications were performed using Genie Pro 2.4 feature extraction software (www.observera.com). Genie Pro uses genetic algorithms to generate solution algorithms that condition the data as input to the classifier. Synthetic bands such as texture, band ratios and edges are created to increase the dimensionality of the data for better classification results. Representative training pixels were collected from multiple image quarter quads to capture and mitigate brightness variations and artifacts resulting from differences in sun angle and radiometric balancing. Three classifications were completed (Genie Pro 2.4) for the study area, each limited to one or two classes against a background. The classifications and corresponding pixel values were: 1. (Background - 0, Water - 1); 2. (Impervious - 0, Vegetation - 1, Soil &amp; Barren - 2); 3. (Background - 0, Tree &amp; Forest - 1). The three classification algorithms were applied to each quarter quad. Obvious errors in each classification were manually corrected. Time varied depending on the quarter quads heterogeneity. Typically, manual correction was limited to 30 minutes to 1 hour per quarter quad. Soil/Impervious Surface confusion and salt-and-pepper grass in forest canopy were the most common errors corrected. A mosaic of each classification was created (ENVI 4.8) and a hierarchical raster calculator expression (ArcGIS 10.2) was used to determine each pixel's final class. Vegetated areas from "classification 2" that were identified as trees/forest in "classification 3" were classified as tree/forest while remaining vegetated areas were classified as grass/herbaceous. Soil/barren and impervious surfaces remained unchanged. Finally areas identified as water in "classification 1" took precedence and were burned into the final land cover mosaic. The land cover mosaic was reclassified using a modified Anderson Level 1 classification similar to that used for the National Land Cover Database 2001 (NLCD) with the following classes: 0 - Unclassified; 10 - Water; 20 - Impervious Surface; 30 - Soil &amp; Barren; 40 - Trees &amp; Forest; 70 - Grass &amp; Herbaceous. **12/2016 UPDATE The prior published Paterson, NJ MULC data included areas beyond the study area boundary. In 2016, this land cover product was clipped to match the 2010 US Census Urban Area boundary plus 1 km buffer. (https://www.epa.gov/enviroatlas/enviroatlas-spatial-extents). Please make sure to use the most up to date version of this land cover product. A sample of 500 completely random points was generated to assess the accuracy of the classified land cover map. The random points were provided to a second analyst who had not been involved with generating the land cover map. The accuracy assessment included the following classes: Water, Impervious Surface, Soil-Barren, Tree, and Grass-Herbaceous. The second analyst performed photo interpretation of the validation points on the original NAIP imagery used to develop the land cover map, assigning a land cover class to each reference pixel. Ancillary image data such as Google Satellite and Street Views, and Bing Aerial and Birdseye views, were used as appropriate to substantiate the interpretation based on the NAIP imagery. Uninterpretable points (e.g., dark shadow) were noted and discarded. This analysis used a fuzzy classification approach (Gopal and Woodcock, 1994). The second analyst recorded her confidence in her interpreted land cover at each point assigning the reference point a value between 1 and 5: 1: Absolutely Wrong: classification value was unacceptable (Very Wrong); 2: Understandable but Wrong: classification value was not good. There was something about the site that made the answer understandable, but there was clearly a better answer. Classification would pose a problem for users of the map. (Not Right); 3: Reasonable or Acceptable: Maybe not the best possible classification but acceptable; the classification did not pose a problem to users of the map. (Right); 4: Good Answer: Would be happy to find this classification given on the map (Very Right); 5: Absolutely Right: No doubt about the match. (Perfect). If any LC classes ended up with less than fifty reference points, a stratified (by LC class) random sample of additional points was generated and interpreted. (This step typically applies only to Soil-Barren, and less frequently Water). Thus in the end, all classes had a minimum of fifty reference samples, and most classes (all but Soil and Water) had approximately 100 reference samples. The final accuracy assessment resulted in confusion matrices for a non-fuzzy method (MAX) and a fuzzy method (RIGHT), both presented below. The fuzzy method allowed for uncertainty in the analyst's photo interpretation due to complex land cover characteristics. For example, for a point located within a pixel on land comprised of patchy grass and soil, the interpreter may have assigned a 4 for grass and a 3 for soil. This was accounted for by the RIGHT results, while MAX only accounted for the highest value recorded by the interpreter. The following error matrix summarizes the MAX accuracy assessment data For easier readability, this XML metadata can be opened in a text editor (e.g., Notepad) and the confusion matrix may be copied from text editor to an Excel spreadsheet. Confusion matrices can also be viewed in original formatting by opening in ArcCatalog: RASTER_TXT Grass_Herb Impervious SoilBarren TreeForest Water N(n) Users Accuracy Errors of Commission Grass_Herb 51 6 0 14 0 71 71.83 28.17 Impervious 16 241 2 13 2 274 87.96 12.04 SoilBarren 1 2 46 1 0 50 92.0 8.0 TreeForest 10 5 0 104 0 119 87.39 12.61 Water 0 1 1 0 48 50 96.0 4.0 N(n) 78 255 49 132 50 564 Producers Accuracy 65.38 94.51 93.88 78.79 96.0 Errors of Omission 34.62 5.49 6.12 21.21 4.0 OVERALL USER'S ACCURACY 86.88 The following error matrix summarizes the RIGHT fuzzy accuracy assessment data For easier readability, this XML metadata can be opened in a text editor (e.g., Notepad) and the confusion matrix may be copied from text editor to an Excel spreadsheet. Confusion matrices can also be viewed in original formatting by opening in ArcCatalog: RASTER_TXT Grass_Herb Impervious SoilBarren TreeForest Water N(n) Users Accuracy Errors of Commission Grass_Herb 58 5 0 8 0 71 81.69 18.31 Impervious 7 257 1 7 2 274 93.8 6.2 SoilBarren 1 0 48 1 0 50 96.0 4.0 TreeForest 3 5 0 111 0 119 93.28 6.72 Water 0 1 1 0 48 50 96.0 4.0 N(n) 69 268 50 127 50 564 Producers Accuracy 84.06 95.9 96.0 87.4 96.0 Errors of Omission 15.94 4.1 4.0 12.6 4.0 OVERALL FUZZY USER'S ACCURACY 92.55 References: Gopal, S. and Woodcock, C. 1994. Theory and Methods for Accuracy Assessment of Thematic Maps Using Fuzzy Sets. Photogrammetric Engineering and Remote Sensing 60(2), 181-188. Entity and Attribute Detail Citation: https://www.epa.gov/enviroatlas/enviroatlas-fact-sheets</gco:CharacterString>
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