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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). For more information about EnviroAtlas data, go to https://www.epa.gov/enviroatlas/enviroatlas-data. For information about the University of Vermont (UVM) Spatial Analysis Lab (SAL), go to https://www.uvm.edu/rsenr/sal/. These data were created by two institutions and shared as part of an interagency agreement between the US Environmental Protection Agency (EPA) and the US Forest Service Urban Tree Canopy Assessment program. The University of Vermont Spatial Analysis Laboratory (SAL), under the direction of Jarlath O'Neil-Dunne, created the majority of the land cover for the study area. EPA added agriculture and wetlands taken from ancillary data sources. This Meter-Scale Urban Land Cover (MULC) dataset for the Chicago Region includes Cook County, DuPage County, Kane County, Kendall County, Lake County, McHenry County, Will County (IL), Lake County, LaPorte County and Porter County (IN). Seven land cover classes were mapped: Water (10), Impervious Surfaces (20), Soil/Barren (30), Trees (40), Grass/Herbaceous (70), Agriculture (80) and Wetlands (Woody [91] and Emergent [92]). The primary sources used to derive this land cover layer were 2006, 2007, 2008, 2010, 2013, 2014 LiDAR data, 2010, 2012, 2013 National Agriculture Imagery Program (NAIP) imagery (U.S. Department of Agriculture) and 2010, 2013 Ortho imagery. UVM SAL Processing Steps: Ancillary data sources included GIS data provided by each county or created by the UVM SAL. Object-based image analysis techniques (OBIA) were employed to extract land cover information using the best available remotely sensed and vector GIS datasets (O'Neil-Dunne, MacFaden, and Royar 2014). OBIA systems work by grouping pixels into meaningful objects based on their spectral and spatial properties, while taking into account boundaries imposed by existing vector datasets. Within the OBIA environment a rule-based expert system was designed to effectively mimic the process of manual image analysis by incorporating the elements of image interpretation (color/tone, texture, pattern, location, size, and shape) into the classification process. A series of morphological procedures were employed to insure that the end product is both accurate and cartographically pleasing. Following the automated OBIA mapping a detailed manual review of the dataset was carried out at a scale of 1:5,000 and all observable errors were corrected. This dataset represents a 'top down' mapping perspective in which tree canopy overhanging other features is assigned to the tree canopy class. EPA Processing Steps: EPA processing steps included: adding Agriculture, Wetlands (Woody and Emergent), and conducting an accuracy assessment. Agriculture - To identify Agriculture (80), 2008 USDA Common Land Unit (CLU) vector data and NAIP and Google imagery were used as guides to determine the areas most likely to be used for cultivated row crops. CLU data delineate agricultural land boundaries based on land use features such as roads and water bodies and, as a result, remain relatively constant over time. Areas that appeared to be Agriculture upon visual inspection of imagery but that were not included in the CLU data were hand digitized. All identified Agriculture areas were converted to raster and mosaicked into the land cover dataset. Wetlands - Wetlands vector data were obtained from the US Fish and Wildlife Service National Wetlands Inventory (NWI) (U.S. Fish and Wildlife Service). These data are updated on an ongoing basis in collaboration with state and local agencies and organizations. The Illinois data were updated in the mid-1980s and the Indiana data were updated in the mid-2000s. These vector data were converted to raster and overlaid on the land cover. Areas of the land cover previously classified as Trees that were located under the wetlands vector data were reclassified as Woody Wetlands (91). Areas of the land cover previously classified as Grass that were located under the wetlands vector data were reclassified as Emergent Wetland (92). ***-------------------------------------------*** Accuracy Assessment - An accuracy assessment was conducted on the completed land cover classification that included the area classified by SAL plus the Agriculture class added by EPA. Wetlands were not included in the accuracy assessment due to difficulties identifying those areas in the imagery per EnviroAtlas accuracy assessment methods. An Analyst performed photointerpretation of the NAIP aerial photography used in the classification. Six hundred random reference points (100 per land cover class) were interpreted and labeled using a fuzzy classification approach (Gopal and Woodcock 1994). This permitted the Analyst to assign a confidence value to the photo interpreted label at each reference point. Confidence is expressed as an integer from 1 to 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 it was 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) After the initial assessment, additional samples were generated for any class with less than 50 reference samples. Using stratified random sampling, sufficient sample points were generated such that all classes had a minimum of fifty reference samples (most classes had approximately 100 reference samples). In total, 97 points were added and included in the final accuracy assessment. The final accuracy assessment resulted in confusion matrices for non-fuzzy method ("MAX") and fuzzy method ("RIGHT"), both presented below. MAX was a more conservative view and RIGHT was a more liberal view. The MAX interpretation was correct if the classified land cover matched the interpreter's highest score, illustrating that the interpreter found this class to be the most appropriate for that location. The RIGHT interpretation was correct if the classified land cover matched any class the interpreter gave a value of 3 or greater, illustrating that the interpreter found the classification to be acceptable but another class may have been more appropriate. This 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 confusion matrices summarize the accuracy assessment MAX and RIGHT results. 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: MAX Agricult Grass_Herb Impervious SoilBarren TreeForest Water Row Total User's Accuracy Agricult 175 10 0 0 1 0 186 0.94086 Grass_Herb 18 114 23 3 22 0 180 0.633333 Impervious 0 3 83 3 2 0 91 0.912088 SoilBarren 0 4 8 35 1 2 50 0.7 TreeForest 0 17 10 0 98 1 126 0.777778 Water 0 3 1 0 1 55 60 0.916667 Row Total 193 151 125 41 125 58 693 Producer's Accuracy 0.906736 0.754967 0.664 0.853659 0.784 0.948276 Overall Accuracy 0.808081 K_Hat 0.760299 K Variance 0.000348 RIGHT Agricult Grass_Herb Impervious SoilBarren TreeForest Water Row Total User's Accuracy Agricult 175 10 0 0 1 0 186 0.94086 Grass_Herb 1 139 18 2 20 0 180 0.772222 Impervious 0 1 87 1 2 0 91 0.956044 SoilBarren 0 3 6 38 1 2 50 0.76 TreeForest 0 9 9 0 107 1 126 0.849206 Water 0 2 1 0 1 56 60 0.933333 Row Total 176 164 121 41 132 59 693 Producer's Accuracy 0.994318 0.847561 0.719008 0.926829 0.810606 0.949153 Overall Accuracy 0.868687 K_Hat 0.836098 K Variance 0.000255 Classification errors may stem from multiple sources. Some are due simply to mixing land cover and land use in the analysis. For example, Agriculture-Grass or Agriculture-Soil confusion are mostly artifacts. Agriculture land use is also Soil land cover while barren, and Grass-Herbaceous land cover while growing row crops. Grass-Soil is the most common confusion due to intermixing and the presence of brown, senescent grass or sparse grass. An underlying assumption is that most non-arid region soil (not barren rock) is capable of supporting some Grass-Herbaceous vegetation at some point during the year. Grass-Tree confusion and Soil-Impervious confusion are also relatively common. This is perhaps a less problematic error than Grass-Impervious, or Tree-Impervious. Grass and Tree are both living vegetation, versus non-living Impervious surfaces. 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. O'Neil-Dunne J, MacFaden S, Royar A. (2014). A Versatile, Production-Oriented Approach to High-Resolution Tree-Canopy Mapping in Urban and Suburban Landscapes Using GEOBIA and Data Fusion. Remote Sens. 2014, 6, 12837-12865. http://www.mdpi.com/2072-4292/6/12/12837. U.S. Department of Agriculture. National Agriculture Imagery Program imagery. Farm Service Agency. Aerial Photography Field Office: U.S. Department of Agriculture Web page, http://www.fsa.usda.gov/FSA/apfoapp?area=home&amp;subject=prog&amp;topic=nai. U.S. Fish and Wildlife Service. Illinois and Indiana National Wetlands Inventory digital data. Accessed 2016. http://wetlands.fws.gov/. Entity and Attribute Detail Citation: https://www.epa.gov/enviroatlas/enviroatlas-fact-sheets</gco:CharacterString>
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