Building blocks for the LiDAR-AGB manuscript…
Figure 1: GPO-LiDAR region component coverages, colored by year of acquisistion and labeled by ID numbers in Table 1.
ID | Name | Year | Area (ha) | PD | AOA | Calibration | Assessment |
---|---|---|---|---|---|---|---|
1 | Erie, Genesee & Livingston | 2019 | 555,853 | 2.04 | 97.72 | 11 | 19 |
2 | Fulton, Saratoga, Herkimer & Franklin | 2018 | 557,421 | 1.98 | 99.61 | 39 | 36 |
3 | Southwest B | 2018 | 560,675 | 1.73 | 98.06 | 28 | 39 |
4 | Cayuga & Oswego | 2018 | 438,201 | 2.78 | 96.89 | 25 | 31 |
5 | Southwest | 2017 | 432,841 | 1.73 | 98.53 | 33 | 37 |
6 | Franklin & St. Lawrence | 2017 | 1,014,527 | 2.69 | 99.24 | 104 | 116 |
7 | Oneida Subbasin | 2017 | 303,986 | 2.1 | 96.02 | 15 | 24 |
8 | Allegany & Steuben | 2016 | 333,590 | 1.69 | 97.77 | 32 | 37 |
9 | Columbia & Rensselaer | 2016 | 248,839 | 1.69 | 98.19 | 17 | 31 |
10 | Clinton, Essex & Franklin | 2015 | 677,727 | 2.23 | 98.7 | 115 | 118 |
11 | Warren, Washington & Essex | 2015 | 618,275 | 2.78 | 99.37 | 106 | 111 |
12 | Madison & Otsego | 2015 | 478,939 | 2.13 | 99.24 | 56 | 75 |
13 | 3 County | 2014 | 768,203 | 2.04 | 96.12 | 92 | 137 |
14 | Long Island | 2014 | 315,542 | 2.04 | 94.77 | 22 | 82 |
15 | Schoharie | 2014 | 275,154 | 2.04 | 95.12 | 31 | 51 |
16 | NYC | 2014 | 83,269 | 1.54 | 90.4 | 2 | 25 |
17 | Great Lakes | 2014 | 574,551 | 2.04 | 98.47 | 73 | 105 |
Total | 8,237,594 | 98.12 | 801 | 1,074 |
LCPRI | Num Plots | Mean Ref. AGB | Area | Mean Map AGB | Total Map AGB | AOA |
---|---|---|---|---|---|---|
Barren | 1 | 0.00 | 23,372 | 13.35 | 0.31 | 94.38 |
Developed | 4 | 0.00 | 587,505 | 52.37 | 30.77 | 92.84 |
Grass/Shrub | 12 | 30.68 | 198,487 | 45.95 | 9.12 | 98.17 |
Water | 17 | 0.00 | 176,963 | 21.22 | 3.76 | 92.68 |
Wetland | 36 | 115.13 | 615,190 | 74.30 | 45.71 | 97.64 |
Cropland | 132 | 1.98 | 1,750,531 | 14.21 | 24.87 | 98.25 |
Tree cover | 599 | 137.97 | 4,236,729 | 127.97 | 542.16 | 98.13 |
Figure 2: a) LINMOD AGB prediction surfaces reflecting a temporal patchwork of conditions; b) Warren, Washington & Essex LINMOD AGB (2015); c) Cayuga & Oswego LINMOD AGB (2018).
Scale | Dist | n | PPH | % RMSE | RMSE | MAE | MBE | R2 |
---|---|---|---|---|---|---|---|---|
Plot Pixel | 709 | 33.28 | 37.23 (0.05) | 26.39 (0.99) | 0.40 (1.40) | 0.78 | ||
8660 | 10 | 514 | 1.38 | 32.21 | 35.55 (0.07) | 25.12 (1.11) | 0.12 (1.57) | 0.79 |
54126 | 25 | 191 | 3.71 | 25.58 | 28.06 (0.18) | 18.53 (1.53) | -1.24 (2.03) | 0.82 |
216506 | 50 | 68 | 10.43 | 17.14 | 18.47 (0.24) | 13.03 (1.60) | -1.18 (2.25) | 0.90 |
Figure 3: 1:1 plots comparing modeled predictions to FIA estimates across selected scales, represented by distances between hexagon centroids (rows). Geometric Mean Functional Regression trend line shown with dashed (orange) line, and 1:1 line shown with solid (red) line.
Figure 4: Summary assessment metrics (as defined in section X) comparing LINMOD mapped predictions to FIA estimates as a function of aggregation unit size (described by distances between hexagon centroids). Red trend lines produced using LOESS method.
Figure 5: Comparison of mapped LINMOD predictions to FIA estimates and associated 95% confidence interval within standardized aggregation hexagons. FIA estimates of AGB are scaled by the proportion of forest cover indicated by LCMAP 2016 tree cover, wetland, croplands and grasslands classified pixels. FIA estimates exceeding 425 Mg/Ha (max plot level observation in our training data) were excluded from the analysis as they are artifacts of the forest cover scaling procedure. Observations are sorted by increasing FIA estimates along the x-axis. RMSE, MAE, MBE in Mgha\(^{-1}\) as defined in section X; % RMSE computed as RMSE divided by the mean FIA standard estimates across standard hexagons. % Outside reflects the percentage of FIA standard hexagons where our aggregate predictions fell outside the FIA 95% confidence interval.
Figure 6: LINMOD plot to pixel residuals summarized at units spaced 50km apart. Hexagons with only one reference plot removed. a) Max of FIA plot-level AGB estimates Mgha\(^{-1}\) b) Standard Deviation of FIA plot-level AGB estimates Mgha\(^{-1}\) c) MBE Mgha\(^{-1}\) d) RMSE Mgha\(^{-1}\) e) Hex-level MBE as a function of max reference value within each hex f) Hex-level RMSE as a function of Hex-level standard deviation. Red trend lines in e & f produced with least squares regression. MBE and RMSE as defined in section X.
Predictor | Definition | Group |
---|---|---|
H0, H10, … H100, H95, H99 | Decile heights of returns, in meters, as well as 95th and 99th percentile return heights. | LiDAR |
D10, D20… D90 | Density of returns above a certain height, as a proportion. After return height is divided into 10 equal bins ranging from 0 to the maximum height of returns, this value reflects the proportion of returns at or above each breakpoint. | LiDAR |
N | Number of returns at a given plot or pixel | LiDAR |
ZMEAN, ZMEAN_C | Mean height of all returns (ZMEAN) and all returns above 2.5m (ZMEAN_C) | LiDAR |
Z_KURT, Z_SKEW | Kurtosis and skewness of height of all returns | LiDAR |
QUAD_MEAN, QUAD_MEAN_C | Quadratic mean height of all returns (QUAD_MEAN) and all returns above 2.5m (QUAD_MEAN_C) | LiDAR |
CV, CV_C | Coefficient of variation for heights of all returns (CV) and all returns above 2.5m (CV_C) | LiDAR |
L2, L3, L4, L_CV, L_SKEW, L_KURT | L-moments and their ratios as defined by Hosking (1990), calculated for heights of all returns | LiDAR |
CANCOV | Ratio of returns above 2.5m to all returns (Pflugmacher et al. 2012) | LiDAR |
HVOL | CANCOV * ZMEAN (Pflugmacher et al. 2012) | LiDAR |
RPC1 | Ratio of first returns to all returns (Pflugmacher et al. 2012) | LiDAR |
TMIN, TMIN, PRECIP | Climate variables in the form of 30 year normals (1980-2010) for minimum and maximum annual temperature (C) and average annual precipitation (mm) from Daly (2008) | Climate |
ELEV, SLOPE, ASPECT, TWI | Topographic variables computed from a 30m DEM downloaded using the terrainr package (Mahoney 2021) | Topography |
TAX_CODE_* | Individual tax code classifications as defined by NYS Department of Taxation and Finances (2019) | Tax |
TAX_CATEGORY_* | Broad grouping of tax codes as defined by NYS Department of Taxation and Finances (2019) | Tax |
RF | GBM | SVM | LINMOD | |
---|---|---|---|---|
RMSE | 40.55 | 41.02 | 41.63 | 41.07 |
% RMSE | 37.34 | 37.78 | 38.34 | 37.82 |
MBE | 3.14 | 1.05 | -1.90 | 3.10 |
R\(^2\) | 0.75 | 0.74 | 0.73 | 0.74 |
Figure 7: Predicted vs observed scatter plot and 1:1 line for four component models against the holdout portion of the calibration dataset. AGB values in Mgha\(^{-1}\).
Scale | Dist | n | PPH | Model | % RMSE | RMSE | MAE | MBE | R2 |
---|---|---|---|---|---|---|---|---|---|
Plot Pixel | 709 | RF | 33.52 | 37.49 (0.05) | 26.85 (0.98) | 0.52 (1.41) | 0.77 | ||
GBM | 33.42 | 37.38 (0.05) | 26.70 (0.98) | -0.83 (1.40) | 0.77 | ||||
SVM | 34.51 | 38.60 (0.06) | 26.47 (1.06) | -4.62 (1.44) | 0.76 | ||||
LINMOD | 33.28 | 37.23 (0.05) | 26.39 (0.99) | 0.40 (1.40) | 0.78 | ||||
8660 | 10 | 514 | 1.38 | RF | 32.32 | 35.67 (0.06) | 25.50 (1.10) | 0.32 (1.57) | 0.78 |
GBM | 32.07 | 35.40 (0.07) | 25.10 (1.10) | -1.14 (1.56) | 0.79 | ||||
SVM | 33.58 | 37.06 (0.08) | 25.34 (1.19) | -5.03 (1.62) | 0.77 | ||||
LINMOD | 32.21 | 35.55 (0.07) | 25.12 (1.11) | 0.12 (1.57) | 0.79 | ||||
54126 | 25 | 191 | 3.71 | RF | 25.01 | 27.44 (0.17) | 18.57 (1.47) | -1.15 (1.99) | 0.83 |
GBM | 25.81 | 28.31 (0.19) | 18.97 (1.52) | -2.36 (2.05) | 0.82 | ||||
SVM | 27.76 | 30.45 (0.21) | 19.85 (1.67) | -6.42 (2.16) | 0.79 | ||||
LINMOD | 25.58 | 28.06 (0.18) | 18.53 (1.53) | -1.24 (2.03) | 0.82 | ||||
216506 | 50 | 68 | 10.43 | RF | 16.73 | 18.03 (0.22) | 13.05 (1.52) | -0.95 (2.20) | 0.91 |
GBM | 17.54 | 18.91 (0.24) | 13.55 (1.61) | -2.01 (2.30) | 0.90 | ||||
SVM | 20.27 | 21.85 (0.30) | 15.44 (1.89) | -6.54 (2.55) | 0.86 | ||||
LINMOD | 17.14 | 18.47 (0.24) | 13.03 (1.60) | -1.18 (2.25) | 0.90 |
Figure 8: 1:1 plots comparing modeled predictions to FIA estimates across selected scales, represented by distances between hexagon centroids (rows), and all models (columns). Geometric Mean Functional Regression trend line shown with dashed (orange) line, and 1:1 line shown with solid (red) line.
Figure 9: Global spatial autocorrelation (Moran’s I) of LINMOD mapped residuals as a function of search radius. Red dashed upper and lower envelopes represent the 95% interval computed from 1000 bootstrap iterations of randomly re-assigning plot locations.
Figure 10: Smoothed kernel density estimates of model-based bootstrap standard errors for LINMOD aggregate predictions across six size groupings. Aggregate predictions and estimates of standard error were computed for 1000 randomly sampled polygons with sizes from 1-500 hectares.
Figure 11: Bootstrap bias summaries comparing the original model aggregate prediction to the average aggregate prediction across all bootstrap iterations for six size groupings. Aggregate predictions and estimates of bootstrap bias were computed for 1000 randomly sampled polygons with sizes from 1-500 hectares.
If you see mistakes or want to suggest changes, please create an issue on the source repository.
For attribution, please cite this work as
Johnson (2022, March 21). CAFRI Labs: LiDAR-AGB Draft Tables and Figures. Retrieved from https://cafri-labs.github.io/acceptable-growing-stock/posts/lidar-agb-draft-tables-and-figures/
BibTeX citation
@misc{johnson2022lidar-agb, author = {Johnson, Lucas}, title = {CAFRI Labs: LiDAR-AGB Draft Tables and Figures}, url = {https://cafri-labs.github.io/acceptable-growing-stock/posts/lidar-agb-draft-tables-and-figures/}, year = {2022} }