Table 1. The four rectangular (in WGS 84 / UTM zone 35N, EPSG:32635) study areas named after the regions where they were located in Finland, and the Sentinel-2 MSI Level-2A products used in the study. The sun zenith angle corresponds approximately to the centre of the study area at the time of Sentinel-2 MSI image acquisition. Numbers in the size column are rounded to the closest kilometre. | |||||
Name | Easting (m) | Size | Sun zenith angle | Sentinel-2 MSI Level-2A products | |
min | max | ||||
Northing (m) | |||||
min | max | ||||
Central Finland | 373960 | 444960 | 71 km × 79 km | 39.7° | S2A_MSIL2A_20190630T100031_N0212_R122_T35VLK_20190630T125130, S2A_MSIL2A_20190630T100031_N0212_R122_T35VMK_20190630T125130 |
6900320 | 6979320 | ||||
North Savo | 526580 | 579340 | 53 km × 44 km | 40.6° | S2A_MSIL2A_20190614T094031_N0212_R036_T35VNL_20190614T111852 |
7043660 | 7087340 | ||||
South Karelia | 527900 | 600900 | 73 km × 59 km | 38.1° | S2A_MSIL2A_20200615T093041_N0214_R136_T35VNH_20200615T120311 |
6728920 | 6787920 | ||||
Kanta-Häme | 306000 | 403800 | 98 km × 79 km | 38.8° | S2A_MSIL2A_20190710T100031_N0213_R122_T35VLH_20190710T114201 |
6718240 | 6797040 |
Table 2. Forest characteristics of the field plots used for each study area. Plot level mean values for diameter, tree height, basal area, stem volume and stem count are given. The second given value in the brackets is the interquartile range, which is defined as the difference between the 75th and 25th percentiles of the data. Forest reflectances were simulated using forest reflectance and transmittance model FRT for these field plots. | ||||||
Study area | Number of sampling windows | Mean diameter (cm) | Mean tree height (m) | Mean basal area (m2 ha–1) | Mean stem volume (m3 ha–1) | Mean stem count (ha–1) |
Central Finland | 430 | 20.4 (7.0) | 17.7 (5.7) | 22.7 (10.7) | 204 (121) | 1028 (550) |
North Savo | 113 | 13.9 (5.1) | 12.1 (4.0) | 16.5 (8.5) | 105 (71) | 1650 (1022) |
South Karelia | 257 | 17.3 (8.0) | 15.8 (7.2) | 23.9 (12.5) | 200 (154) | 1542 (903) |
Kanta-Häme | 127 | 16.7 (8.6) | 15.2 (7.0) | 23.0 (9.7) | 184 (117) | 1664 (1042) |
Table 3. Forest reflectance and transmittance model FRT input parameters and their baseline values. The origin of the value is described in the source column. | ||
Parameter | Baseline values | Source |
Specific leaf weight (g m–2), SLW | Pine 158, Spruce 200, Birch 57 | As used by Hovi et al. (2016) |
Branch area to leaf area ratio, BAILAI | Pine 0.18, Spruce 0.18, Birch 0.15 | As used by Rautiainen and Lukeš (2015) and Hovi et al. (2016) |
Shoot shading coefficient, SSC | Pine 0.59, Spruce 0.64, Birch 1.00 | As used by Rautiainen and Lukeš (2015) and Hovi et al. (2016) |
Shoot length (m), SHL | Pine 0.10, Spruce 0.05, Birch 0.40 | As used by Hovi et al. (2016) |
Tree distribution parameter, TDP | 1.2 for all species | As used by Hovi et al. (2016) |
Tree height (m) | Forest data | Finnish Forest Centre |
Trunk diameter (cm) | Forest data | Finnish Forest Centre |
Density (m–2) | Forest data | Finnish Forest Centre |
Tree species | Forest data | Finnish Forest Centre |
Dry leaf weight (kg tree–1), DLW | Allometric regression models from literature and forest data | Repola (2008, 2009) and Johansson (1999) |
Crown radius (m) | Allometric regression models from literature and forest data | Rautiainen et al. (2008) and Jakobsons (1970) |
Crown length (m) | Allometric regression models from literature and forest data | Rautiainen et al. (2008) and Nilson et al. (1999) |
Table 4. Estimation accuracy (relative root-mean-square error, rRMSE), correlation (Pearson correlation coefficient, r) and bias (normalised mean bias, NMB) for the simulated forest reflectance in eight Sentinel-2 MSI bands (B2–B8A) with the baseline input parameter values (Table 3). | |||||||||
Study area | B2 | B3 | B4 | B5 | B6 | B7 | B8 | B8A | |
Central Finland | r | 0.62 | 0.67 | 0.49 | 0.73 | 0.80 | 0.78 | 0.78 | 0.77 |
rRMSE (%) | 38.8 | 24.5 | 28.8 | 15.9 | 34.0 | 36.2 | 34.8 | 37.4 | |
NMB (%) | 31.4 | 16.4 | 7.2 | 5.0 | 29.6 | 31.9 | 30.9 | 33.7 | |
North Savo | r | 0.58 | 0.50 | 0.61 | 0.61 | 0.77 | 0.76 | 0.75 | 0.74 |
rRMSE (%) | 21.5 | 17.4 | 31.2 | 18.8 | 25.7 | 29.3 | 30.9 | 30.8 | |
NMB (%) | 5.4 | –0.1 | –1.9 | –6.8 | 21.8 | 25.6 | 27.7 | 27.7 | |
South Karelia | r | 0.13 | 0.23 | 0.26 | 0.56 | 0.77 | 0.75 | 0.75 | 0.74 |
rRMSE (%) | 26.9 | 22.8 | 29.1 | 19.3 | 24.0 | 26.7 | 29.2 | 27.5 | |
NMB (%) | –15.7 | –9.4 | –15.0 | –11.5 | 17.4 | 20.8 | 24.3 | 22.7 | |
Kanta-Häme | r | 0.51 | 0.51 | 0.44 | 0.69 | 0.82 | 0.79 | 0.80 | 0.79 |
rRMSE (%) | 21.1 | 26.1 | 26.4 | 19.1 | 26.4 | 24.5 | 23.4 | 25.1 | |
NMB (%) | 5.8 | 15.6 | 12.4 | 11.1 | 21.5 | 19.4 | 18.8 | 20.7 |
Table 5. Estimation accuracy (relative root-mean-square error, rRMSE), correlation (Pearson correlation coefficient, r) and bias (normalised mean bias, NMB) for the simulated forest reflectance in eight Sentinel-2 MSI bands (B2–B8A) with the adjusted set of input parameter values (Fig. 5). | |||||||||
Study area | B2 | B3 | B4 | B5 | B6 | B7 | B8 | B8A | |
Central Finland | r | 0.64 | 0.67 | 0.50 | 0.68 | 0.76 | 0.74 | 0.73 | 0.71 |
rRMSE (%) | 33.0 | 16.2 | 25.9 | 16.0 | 17.8 | 19.3 | 19.1 | 20.7 | |
NMB (%) | 25.7 | 4.1 | 4.3 | –7.0 | 8.1 | 9.9 | 9.8 | 12.6 | |
North Savo | r | 0.58 | 0.49 | 0.60 | 0.57 | 0.74 | 0.73 | 0.71 | 0.70 |
rRMSE (%) | 19.3 | 19.2 | 29.1 | 24.2 | 13.8 | 15.5 | 16.8 | 16.7 | |
NMB (%) | 0.3 | –10.2 | –6.5 | –17.4 | 3.3 | 6.5 | 8.9 | 9.3 | |
South Karelia | r | 0.19 | 0.27 | 0.30 | 0.58 | 0.77 | 0.75 | 0.74 | 0.74 |
rRMSE (%) | 27.8 | 25.9 | 28.7 | 25.4 | 14.4 | 15.2 | 15.6 | 15.0 | |
NMB (%) | –19.4 | –19.1 | –17.1 | –21.8 | –1.8 | 1.0 | 4.4 | 3.5 | |
Kanta-Häme | r | 0.51 | 0.53 | 0.45 | 0.67 | 0.82 | 0.80 | 0.81 | 0.79 |
rRMSE (%) | 19.6 | 17.8 | 24.0 | 13.7 | 12.8 | 13.2 | 12.8 | 13.2 | |
NMB (%) | 1.0 | 3.3 | 9.4 | –1.7 | 1.9 | 0.0 | –0.0 | 1.9 |