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                        <gco:CharacterString>These data were collected using funding from the U.S. Government and can be used without additional permissions or fees. If you use these data in a publication, presentation, or other research product please use the following citation: USDA Forest Service. 2025. USFS Percent Tree Canopy (Science Version) CONUS v2023-5. Salt Lake City, UT. Appropriate use includes regional to national assessments of vegetation cover, land cover, or land use change trends, total extent of vegetation cover, land cover, or land use change, and aggregated summaries of vegetation cover, land cover, or land use change. This product is the initial output from the modeling process. No post-processing (such as applying a minimum mapping unit or manually burning in known features such as roads) has been performed.The USDA Forest Service makes no warranty, expressed or implied, including the warranties of merchantability and fitness for a particular purpose, nor assumes any legal liability or responsibility for the accuracy, reliability, completeness or utility of these geospatial data, or for the improper or incorrect use of these geospatial data. These geospatial data and related maps or graphics are not legal documents and are not intended to be used as such. The data and maps may not be used to determine title, ownership, legal descriptions or boundaries, legal jurisdiction, or restrictions that may be in place on either public or private land. Natural hazards may or may not be depicted on the data and maps, and land users should exercise due caution. The data are dynamic and may change over time. The user is responsible to verify the limitations of the geospatial data and to use the data accordingly.  Additionally, the U.S. Forest Service waives copyright and related rights in the work worldwide through the CC0 (which can be found at https://creativecommons.org/public-domain/cc0/).  In accordance with Federal civil rights law and U.S. Department of Agriculture (USDA) civil rights regulations and policies, the USDA, its Agencies, offices, and employees, and institutions participating in or administering USDA programs are prohibited from discriminating based on race, color, national origin, religion, sex, disability, age, marital status, family/parental status, income derived from a public assistance program, political beliefs, or reprisal or retaliation for prior civil rights activity, in any program or activity conducted or funded by USDA (not all bases apply to all programs). Remedies and complaint filing deadlines vary by program or incident.  Persons with disabilities who require alternative means of communication for program information (e.g., Braille, large print, audiotape, American Sign Language, etc.) should contact the State or local Agency that administers the program or contact USDA through the Telecommunications Relay Service at 711 (voice and TTY). Additionally, program information may be made available in languages other than English.  To file a program discrimination complaint, complete the USDA Program Discrimination Complaint Form, AD-3027, found online at How to File a Program Discrimination Complaint and at any USDA office or write a letter addressed to USDA and provide in the letter all of the information requested in the form. To request a copy of the complaint form, call (866) 632-9992. Submit your completed form or letter to USDA by: (1) mail: U.S. Department of Agriculture, Office of the Assistant Secretary for Civil Rights, 1400 Independence Avenue, SW, Mail Stop 9410, Washington, D.C. 20250-9410; (2) fax: (202) 690-7442; or (3) email: program.intake@usda.gov.  USDA is an equal opportunity provider, employer, and lender.  </gco:CharacterString>
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                        <gco:CharacterString>Model performance metrics including mean of squared residuals and percent variability explained were obtained from the random forest regression model (Breiman, 2001; R Core Team 2024) used to derive tree canopy cover estimates. The maximum mean of squared residuals was 193.6 and the minimum was 90.6. The maximum percent variability explained was 90.1 and the minimum was 60.3. Additionally, 500 random forest trees were used to derive a tree canopy cover prediction for each pixel. Standard errors were calculated for each pixel using the estimates from the 500 trees. The standard errors provide information on the certainty of TCC predictions. We conducted an independent error assessment over the 2011 NLCD TCC v2023.5 map output. Thirty percent of our response data was withheld from model calibration to be used to assess error. In order to account for inconsistencies between the FIA plot location density between different states, along with plots that we did not use due to quality assurance measures, we estimated the area weight of each plot by computing Thiessen polygons for each plot centroid. In order to avoid extremely large weights for edge plots, any plot on the edge assumed the average of the weight of neighboring non-edge plots polygon weights. We then computed the weighted root mean squared error (RMSE) and mean absolute error (MAE) using the reference TCC value as the truth, and the final NLCD TCC 2011 map value as the predicted value.</gco:CharacterString>
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                            <specification>
                                <CI_Citation>
                                    <title gco:nilReason="missing"/>
                                    <date>
                                        <CI_Date>
                                            <date>
                                                <gco:Date>2025-04-01</gco:Date>
                                            </date>
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                                        <CI_Date>
                                            <date>
                                                <gco:Date>2025-04-01</gco:Date>
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                                            <date>
                                                <gco:Date>2025-04-01</gco:Date>
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                            <explanation>
                                <gco:CharacterString>For CONUS the weighted map RMSE is 12.92% and the MAE is 8.22%.</gco:CharacterString>
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                                <gco:Boolean>true</gco:Boolean>
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            <lineage>
                <LI_Lineage>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>The USFS Forest Inventory and Analysis (FIA) program photo-interpreted percent tree canopy cover (TCC) response data. Photointerpretation (PI) measured TCC using a custom ArcGIS plug-in tool (Goeking et al., 2012) from 105-point grids placed in 90x90 squares centered on USFS FIA plot design. A total of 55,242 PI plots were used in TCC modeling.Goeking, S.A., Liknes, G.C., Lindblom, E., Chase, J., Jacobs, D.M., and Benton, R. (2012). A GIS-based tool for estimating tree canopy cover on fixed-radius plots using high-resolution aerial imagery. In: R. Morin, S. Randall, G.C. Liknes (Comps.), Moving from status to trends: Forest Inventory and Analysis (FIA) symposium 2012 December 4-6, Baltimore MD (pp. 237-241). (General Technical Report NRS-P-105). U.S. Department of Agriculture, Forest Service, Northern Research Station. Newtown Square, PA. https://www.fs.fed.us/nrs/pubs/gtr/gtr_nrs-p-105.pdf</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>Photo-interpreted Canopy Cover (FIA)</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2012-01-01T00:00:00</gco:DateTime>
                            </dateTime>
                        </LI_ProcessStep>
                    </processStep>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>Two sets of annual medoid composites were created. Set 1 does not include any Landsat 7 data occurring after 2002. Set 2 includes all available Landsat 7 data through 2015. To generate annual composites Landsat and Sentinel 2 imagery were collected from 1984-2024 from Julian day 153-273 for 1984-2015, and Julian day 182-244 for 2016-2024. Landsat 7 imagery were used from 1999-2002, and not used after 2002 due to scan line correction failure in 2003. For Landsat image collections, the CFmask cloud masking algorithm, an implementation of Fmask 2.0 was applied (Zhu and Woodcock 2012; Foga et al., 2017), and the cloudScore algorithm (Chastain et al., 2019). For Sentinel-2 data, the s2Cloudless algorithm was used to mask clouds (Zupanc, 2017). We used the Temporal Dark Outlier Mask (TDOM) method to mask cloud shadows in both Landsat and Sentinel-2 (Chastain et al., 2019). For each year, the annual geometric medoid was computed to summarize the data into a single annual composite for each of the 54 tiles that span CONUS.Chastain, R., Housman, I., Goldstein, J., Finco, M., and Tenneson, K. (2019). Empirical cross sensor comparison of Sentinel-2A and 2B MSI, Landsat-8 OLI, and Landsat-7 ETM top of atmosphere spectral characteristics over the conterminous United States. In Remote Sensing of Environment (Vol. 221, pp. 274-285). https://doi.org/10.1016/j.rse.2018.11.012Foga, S., Scaramuzza, P.L., Guo, S., Zhu, Z., Dilley, R.D., Beckmann, T., Schmidt, G.L., Dwyer, J.L., Hughes, M.J., and Laue, B. (2017). Cloud detection algorithm comparison and validation for operational Landsat data products. In Remote Sensing of Environment (Vol. 194, pp. 379-390). http://doi.org/10.1016/j.rse.2017.03.026.Zhu, Z., and Woodcock, C.E. (2012). Object-based cloud and cloud shadow detection in Landsat imagery, Remote Sensing of Environment, 118, pp. 83-94.Zupanc, A. (2017) Improving Cloud Detection With Machine Learning. Online: https://medium.com/sentinel-hub/improvingcloud-detection-with-machine-learningc09dc5d7cf13. Accessed 20 November 2022.</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>Annual Landsat-Sentinel2 image composites</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2022-10-01T00:00:00</gco:DateTime>
                            </dateTime>
                        </LI_ProcessStep>
                    </processStep>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>The Landsat-based detection of Trends in Disturbance and Recovery (LandTrendr) temporal segmentation algorithm was applied to the two sets of composite time series in Google Earth Engine (GEE) (Kennedy et al., 2018; Cohen et al., 2018). The resulting two sets of LandTrendr time-series fitted values were used as independent predictor variables in random forest models (Breiman 2001). Stripping artifacts were observed in preliminary modeling of TCC when LandTrendr set 2 visible bands - derived from composite set 2 data that includes all Landsat 7 data through 2015 - were included as predictor layers. To avoid stripping artifacts the visible bands from LandTrendr set 2 fitted values were not used in modeling.Breiman, L. (2001). Random forests. Machine learning (Vol. 45, pp. 15-32). https://doi.org/10.1023/A:1010933404324Cohen, W.B., Yang, Z., Healey, S.P., Kennedy, R.E., and  Gorelick, N. (2018). A LandTrendr multispectral ensemble for forest disturbance detection, Remote Sensing of Environment (Vol. 205, pp. 131-140). https://doi.org/10.1016/j.rse.2017.11.015Kennedy, R., Yang, Z., Gorelick, N., Braaten, J., Cavalcante, L., Cohen, W., and Healey, S. (2018). Implementation of the LandTrendr Algorithm on Google Earth Engine. In Remote Sensing (Vol. 10, Issue 5, p. 691). https://doi.org/10.3390/rs10050691</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>Annual LandTrendr Fitted Images</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2022-10-01T00:00:00</gco:DateTime>
                            </dateTime>
                        </LI_ProcessStep>
                    </processStep>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>Creation of Digital Elevation Model (DEM) derivatives. A CONUS-wide terrain dataset used as a predictor layer was provided by the USGS 3D Elevation Program (U.S. Geological Survey, 2019). Slope, the components of slope, aspect, and the sine and cosine of aspect were calculated for each pixel following industry standards.U.S. Geological Survey. (2019). USGS 3D Elevation Program Digital Elevation Model, accessed August 2022 at https://developers.google.com/earth-engine/datasets/catalog/USGS_3DEP_10m</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>Digital Elevation Model (DEM)</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2022-09-01T00:00:00</gco:DateTime>
                            </dateTime>
                        </LI_ProcessStep>
                    </processStep>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>Creation of cropland data layer (CDL) binary mask. The annual binary agriculture data were produced by classifying all non-tree CDL crops as agriculture and everything else as non-agriculture.USDA National Agricultural Statistics Service Cropland Data Layer. (2024). Published crop-specific data layer [Online]. Available at https://nassgeodata.gmu.edu/CropScape/ (accessed 2024. USDA-NASS, Washington, DC.</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>USDA National Agricultural Statistics Service Cropland Data Layer</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2024-12-01T00:00:00</gco:DateTime>
                            </dateTime>
                        </LI_ProcessStep>
                    </processStep>
                    <processStep>
                        <LI_ProcessStep>
                            <description>
                                <gco:CharacterString>Creation of the percent tree canopy cover (TCC) Science dataset (main process). The CONUS FS Science TCC dataset was created for years 1985 through 2023. For CONUS, 54 tiles were used in a 5x5 moving window where model calibration data was gathered from the moving windows and random forest models were created. The random forest models were applied to the center tiles. The final dataset is a mosaic of TCC valuesFive major steps were employed to map TCC and produce the Science product: 1) collection of reference data, 2) acquisition and/or creation of predictor layers, 3) calibration of random forest regression models for each mapping area using response data and predictor layers, 4) application of those models to predict per-pixel TCC across the entire mapping area, and 5) exporting Science images from Google Earth Engine (GEE) to local computers for further post-processing that includes the creation of the CONUS-wide mosaic. The methodology is described further below, in the technical methods document (Housman et al., 2025), and in an upcoming manuscript in preparation (Heyer et al., in preparation).Step 1: Reference data, consisting of estimated TCC at each of the 63,010 FIA plot locations, were generated via aerial image interpretation of high spatial resolution images collected and supplied by the U.S. Forest Service Forest Inventory and Analysis (FIA) program. The spatial distribution of the sample points follows the FIA systematic grid (Brand et al. 2000). Low quality FIA PI observations were removed for a total of 55,242 FIA plots used in modelingStep 2: Predictor layers include two sets of LandTrendr fitted images spectral derivatives. Set 1 (no Landsat 7 data after 2002) includes all optical bands and indices. Set 2 (includes all Landsat 7 data through 2015) excludes Landsat 7 visible bands to avoid stripping artifacts. Other predictor layers include a binary agriculture layer (1=agriculture, 0 = non-agriculture), elevation data, and terrain derivatives (slope, aspect, sine of aspect, cosine of aspect). The processes for creating the derived layers are described separately (see related Process Steps).Step 3: For each 480 km x 480 km moving window tile, a random forest model was built from 2011 response and predictor data that fell over a 5x5 tile neighborhood for that tile. Models were generated locally using the random forest regression algorithm "sklearn.ensemble.RandomForestRegressor" from the Scikit-Learn package in python (Pedregosa et al. 2011).Step 4: In Google Earth Engine (GEE), models were applied to each tile for CONUS, producing a 2-layered Science image. The first layer was the random forest mean predicted TCC value and the second layer was the standard error (SE), which is the per-pixel standard error of the random forest regression predictions from the individual regression trees. In addition to the model output, a statistic that normalized the expected error, which we refer to as tau (Coulston et al., 2016), was calculated for each processing area. The tau statistics can be used to mask erroneous pixels as described in Coulston et al. (2016). The tau statistics are provided in the supplemental metadata.Step 5: Following model application, the Science TCC images were exported from GEE to local computers for post-processing. During post-processing, mosaics were created, cloud optimized GeoTIFFs (COGs) were generated, statistics were calculated, pyramid layers were built, and color ramps were applied to each Science TCC image. For each Science TCC image, the non-area processing value is 254, and the background value is 255.Brand, G.J., Nelson, M.D., Wendt, D.G., and Nimerfro, K.K. (2000). The hexagon/panel system for selecting FIA plots under an annual inventory. In: McRoberts, R.E.; Reams, G.A.; Van Deusen, P.C., eds. Proceedings of the First Annual Forest Inventory and Analysis Symposium; Gen. Tech. Rep. NC-213. St. Paul, MN: U.S. Department of Agriculture, Forest Service, North Central Research Station: 8-13Breiman, L. (2001). Random forests. Machine Learning (Vol. 45, pp. 5-32)Coulston, J.W., Blinn, C. E., Thomas, V. A., and Wynne, R. H. (2016). Approximating prediction uncertainty for random forest regression models. Photogrammetric Engineering and Remote Sensing, (Vol. 82, Issue 3, pp. 189-197.Heyer, J., Schleeweis, K., Ruefenacht, B., Housman, I., Megown, K., and Bogle, M. In preparation. A time invariant modeling approach to produce annual tree-canopy cover for the conterminous United States. Salt Lake City, UT: U.S. Department of Agriculture, Forest Service, Field Services and Innovation Center Geospatial Office. [Manuscript in Preparation]Housman, I.W.; Bogle, S; Heyer, J.P.; Heyer, J.P.; Megown, K.; Reischmann, J.; Ruefenacht, B.; Ryerson, D.; Schleeweis, K.; 2025. National Land Cover Database Tree Canopy Cover Methods v2023.5. FSIC-GO-10268-RPT1. Salt Lake City, UT: U.S. Department of Agriculture, Forest Service, Field Services and Innovation Center Geospatial Office. 24 p.Pedregosa, F., Varoquaux, G., Gramfort, A., Michel, V., Thirion, B., Grisel, O., Blondel, M., Prettenhofer, P., Weiss, R., Dubourg, V., Vanderplas, J., Passos, A., Cournapeau, D., Brucher, M., Perrot, M. and Duchesnay, E. (2011). Scikit-learn: Machine Learning in Python. In Journal of Machine Learning Research (Vol. 12, pp. 2825-2830)</gco:CharacterString>
                            </description>
                            <rationale>
                                <gco:CharacterString>USFS Percent Tree Canopy Cover (Science Version)</gco:CharacterString>
                            </rationale>
                            <dateTime>
                                <gco:DateTime>2025-04-01T00:00:00</gco:DateTime>
                            </dateTime>
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                    </processStep>
                </LI_Lineage>
            </lineage>
        </DQ_DataQuality>
    </dataQualityInfo>
    <metadataConstraints>
        <MD_LegalConstraints>
            <accessConstraints>
                <MD_RestrictionCode codeList="http://www.isotc211.org/2005/resources/Codelist/gmxCodelists.xml#MD_RestrictionCode" codeListValue="otherRestrictions" codeSpace="ISOTC211/19115">otherRestrictions</MD_RestrictionCode>
            </accessConstraints>
            <otherConstraints>
                <gco:CharacterString>The USDA Forest Service makes no warranty, expressed or implied, including the warranties of merchantability and fitness for a particular purpose, nor assumes any legal liability or responsibility for the accuracy, reliability, completeness or utility of these geospatial data, or for the improper or incorrect use of these geospatial data. These geospatial data and related maps or graphics are not legal documents and are not intended to be used as such. The data and maps may not be used to determine title, ownership, legal descriptions or boundaries, legal jurisdiction, or restrictions that may be in place on either public or private land. Tree Canopy Cover changes may or may not be depicted on the data and maps, and land users should exercise due caution. The data are dynamic and may change over time. The user is responsible to verify the limitations of the geospatial data and to use the data accordingly.</gco:CharacterString>
            </otherConstraints>
        </MD_LegalConstraints>
    </metadataConstraints>
</MD_Metadata>
