Documentation Revision Date: 2017-09-27
Data Set Version: 1
Summary
The fire progression map was made using an algorithm that enabled an assessment of wildfire progression rates at a daily time scale. Fire progression was based on observed active fire detections from both the Terra and Aqua satellites using the MODIS active fire product (MCD14ML; Giglio et al. 2003). The fire progression map enabled an assessment of wildfire progression rates at a daily time step.
This data set includes one fire progression map in a compressed shapefile (.shp within a .zip file). The field data are provided in seven comma-separated (.csv) files. The shapefile data are also provided as a companion file in .kmz format for viewing in Google Earth.
Citation
Bourgeau-Chavez, L.L., S. Endres, L. Jenkins, M. Battaglia, E. Serocki, and M. Billmire. 2017. ABoVE: Burn Severity, Fire Progression, and Field Data, NWT, Canada, 2015-2016. ORNL DAAC, Oak Ridge, Tennessee, USA. https://doi.org/10.3334/ORNLDAAC/1548
Table of Contents
- Data Set Overview
- Data Characteristics
- Application and Derivation
- Quality Assessment
- Data Acquisition, Materials, and Methods
- Data Access
- References
Data Set Overview
This data set provides a fire progression map for year 2015 and measures of burn severity and vegetation community biophysical data collected from areas that were burned by wildfires in 2014 and 2015 in the Northwest Territories, Canada. Field data collected in 2016 include an estimate of burn severity, seedling/sprouting data, soil moisture, peat depth, thaw depth, and vegetation cover for selected sites.
The fire progression map was made using an algorithm that enabled an assessment of wildfire progression rates at a daily time scale. Fire progression was based on observed active fire detections from both the Terra and Aqua satellites using the MODIS active fire product (MCD14ML; Giglio et al. 2003). The fire progression map enabled an assessment of wildfire progression rates at a daily time step.
Project: Arctic-Boreal Vulnerability Experiment (ABoVE)
The Arctic-Boreal Vulnerability Experiment is a NASA Terrestrial Ecology Program field campaign taking place in Alaska and western Canada between 2016 and 2021. Climate change in the Arctic and Boreal region is unfolding faster than anywhere else on Earth, resulting in reduced Arctic sea ice, thawing of permafrost soils, decomposition of long-frozen organic matter, widespread changes to lakes, rivers, coastlines, and alterations of ecosystem structure and function. ABoVE seeks a better understanding of the vulnerability and resilience of ecosystems and society to this changing environment.
Related data set
ABoVE: Burn Severity, Fire Progression, Landcover and Field Data, NWT, Canada, 2014. ORNL DAAC, Oak Ridge, Tennessee, USA. http://dx.doi.org/10.3334/ORNLDAAC/1307
This related data set provides peat landcover maps, fire progression maps, burn severity, and vegetation community biophysical data from areas in the Northwest Territories that were burned by wildfires in 2014.
Data Characteristics
Spatial Coverage: Northwest Territories, Canada. Partial coverage in North Slave, South Slave, and Dehcho Regions of Northwest Territories, Canada.
Domain: Core ABoVE
State/territory: NWT
Grid cells: Ah2v1.Bh0v5, Ah2v1.Bh1v4, Ah2v1.Bh1v5, Ah2v1.Bh2v5, and Ah2v2.Bh0v0
Region: Partial coverage in North Slave, South Slave, and Dehcho Regions
Locale: Yellowknife
Spatial Resolution
Fire progression map (shapefile) at 1 km resolution.
Validation field sites are points in the center of 0.5 acre plots.
Above ground biomass, biophysical site characteristics, burn severity, soil moisture, and seedling/sapling data were collected in six plots along two transects representing a 1 ha site.
Temporal Coverage
Field data were collected from 2016-07-09 to 2016-08-08.
Fire progression map covers the period 2015-05-20 to 2015-08-13.
Study Area: (all latitudes and longitudes given in decimal degrees)
Site (Region) | Westernmost Longitude | Easternmost Longitude | Northernmost Latitude | Southernmost Latitude |
---|---|---|---|---|
Northwest Territories, Canada | -135.542822 | -106.759164 | 68.326948 | 59.927009 |
Data File Information
There is one fire progression file in a compressed shapefile (.zip) format. Individual wildfire progression maps can be extracted from this shapefile. The field data are provided in seven comma-separated (.csv) files. The fire progression data are also provided in .kmz format for viewing in Google Earth.
The focus area of this study includes the 2014 NWT fires (ZF17, ZF20, SS3, SS15) and 2015 NWT Fires (ZF14, ZF2, SS50, SS81, SS28).
Most burned areas were divided into multiple sites (for example, SS3-64). Not all areas were visited for all measurements. Refer to Table 4 for a listing of the sites and type of measurements taken which correspond to the .csv data files.
Table 1. File names and descriptions
File names | Descriptions |
---|---|
2015_NWT_fireprogression.zip | When unzipped, provides fire progression data for year 2015 in a shapefile. The data are also provided as a companion file in .kmz format for viewing in Google Earth. |
NWT_wildfires_burn_severity_2016.csv | Provides observations of burn severity, adventitious root height, and landcover data. Photos of the plots are noted by number and camera ID in this file. |
NWT_wildfires_biophysical_2016.csv | Provides biophysical and ground cover data. |
NWT_wildfires_Seedling_Sprouting_2016.csv | Provides observations of vegetation seedling/saplings and sprouting of mosses and lichen. |
NWT_wildfires_inventory_2016.csv | Provides site/plot observations, species inventory, diameter, and height. |
NWT_wildfires_SoilMoisture_HydrosenseI_2016.csv | Provides soil data using a Hydrosense I instrument. |
NWT_wildfires_SoilMoisture_HydrosenseII_2016.csv | Provides soil data using a Hydrosense II instrument. |
NWT_wildfires_fieldvalidation_2016.csv | Provides vegetation observations from validation sites. |
Fire Progression Map
The fire progression map is provided in the compressed shapefile, 2015_NWT_fireprogression.zip. This shapefile shows the overall spatial extent and date (DOY) burned of 1-km pixels of selected fires over the period 2015-05-20 to 2015-08-13. Fire progression was based on observed active fire detections from both the Terra and Aqua satellites using the MODIS active fire product.
Table 2. Attributes of shapefile: 2015_NWT_fireprogression.shp.
FID | Shapefile feature |
Shape | Feature type (polygon) |
Date | Date burned |
id | Monitoring trends in burn severity index ID |
fire_code | Year of burn and district-fire number |
fire_name | Year of burn and district-fire number (same as fire_code) |
fuelbed_ec | Ecoregion parameter (“western or “southern”; all “western”) |
fuel_moist | 1000-hr fuel moisture (all 0) |
fuel_moi_1 | duff_fuel_moisture (all 0) |
Julian | Day of the year |
Month | Month |
Table 3. Spatial Parameters: 2015_NWT_fireprogression.shp
Geographic coordinate system: GCS_WGS_1984 |
Angular Unit: Degree (0.0174532925199433) |
Prime Meridian: Greenwich (0.0) |
Datum: D_WGS_1984 |
Extent of 2015_NWT_fireprogression.shp
West | East | North | South |
-135.542822 | -106.759164 | 68.326948 | 59.927009 |
Field Data
There are seven comma-separated files (.csv) of burn severity, inventory, seedling/sapling, soil moisture, and biophysical data collected in 2016 from selected 2014 and 2015 wildfire areas.
Burn severity was measured at 27 sites located in wildfire areas. Refer to Table 4 for a listing of the areas for all files. Different sites within each area are not listed in the table.
Note: Photos were taken at the sites and are provided in companion files. A description of the companion files is provided at the end of this section.
Table 4. Summary listing of wildfire areas and data types collected at each site.
Area | Burn Severity | Biophysical | Seedlings | Inventory | Validation | Soil measurements-Hydrosense 1 | Soil measurements-Hydrosense 2 |
---|---|---|---|---|---|---|---|
SSO | X | X | |||||
SS3 | X | X | X | X | X | X | |
SS27 | X | X | X | ||||
SS28 | X | X | X | X | X | X | X |
SS37 | X | X | X | ||||
SS50 | X | X | X | X | X | X | X |
SS81 | X | X | X | X | X | X | X |
ZF2 | X | X | X | X | X | X | |
ZF14 | X | X | X | X | X | X | X |
ZF17 | X | X | X | X | X | X | |
ZF20 | X | X | X | X | X | X |
Burn Severity Data:
This file provides burn severity data collected from 27 locations in eight wildfire areas in July and August of 2016. Data not reported are recorded as -9999 or not_provided.
NOTE: For variables nadircover_: Nadir cover is from a birds-eye view of the plot so multiple layers are not considered and thus all nadir cover values must add to no more than 100 percent.
Table 5. File: NWT_wildfires_burn_severity_2016.csv
Column # | Variable | Units | Description |
---|---|---|---|
1 | site | Unique name given to a field site. The initial alphanumeric code indicates site and fire number and the second part of the name is a site code designated by the research team. | |
2 | plot | Plot number within the site; there are up to 6 plots per site | |
3 | date | YYYYMMDD | Sampling date |
4 | time | HH:MM | Time at which field work began in local time (MDT) |
5 | fire_history | ||
latitude | decimal degrees | Latitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner | |
6 | longitude | decimal degrees | Longitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner |
7 | observer | Initials of person(s) who collected the data | |
8 | ecosystem | Type of ecosystem; where the site included multiple ecosystem types they are all reported. See documentation for ecosystem characteristics. | |
9 | field_notes_ecosystem | ||
10 | thaw_depth | cm | Depth of soil to frozen ground layer reported in centimeters from surface |
11 | peat_depth | cm | Thickness of organic peat soil layer reported in centimeters |
12 | ash | Amount of ash present on ground surface. Reported as: No, Light, Moderate, or Heavy | |
13 | moss_unburned | percent | Percent of moss in plot (10 x 10-m area) that is unburned |
14 | moss_singed | percent | Percent of moss in plot (10 x 10-m area) that is singed |
15 | moss_light | percent | Percent of moss in plot (10 x 10-m area) that is lightly burned |
16 | moss_moderate | percent | Percent of moss in plot (10 x 10-m area) that is moderately burned |
17 | moss_severe | percent | Percent of moss in plot (10 x 10-m area) that is severely burned |
18 | litter_unburned | percent | Percent of litter in plot (10 x 10-m area) that is unburned |
19 | litter_singed | percent | Percent of litter in plot (10 x 10-m area) that is lightly singed |
20 | litter_charred | percent | Percent of litter in plot (10 x 10-m area) that is charred |
21 | litter_ashed | percent | Percent of litter in plot (10 x 10-m area) that is ashed |
22 | shrub_unburned | percent | Percent of shrubs in plot (10 x 10-m area) that is unburned |
23 | shrub_scorched | percent | Percent of shrubs in plot (10 x 10-m area) that is lightly scorched |
24 | shrub_limbs | percent | Percent of shrubs in plot (10 x 10-m area) with some limbs left |
25 | shrub_consumed | percent | Percent of shrubs in plot (10 x 10-m area) that is consumed |
26 | live_trees | percent | Percent of trees in plot (10 x 10-m area) live and undamaged |
27 | dead_foliage_intact | percent | Percent of trees in plot (10 x 10-m area) dead but with no foliage consumed |
28 | dead_foliage_burned | percent | Percent of trees in plot (10 x 10-m area) dead with needles and small branches burned |
29 | dead_trees_secondary | percent | Percent of trees in plot (10 x 10-m area) dead with only some secondary branches remaining |
30 | dead_trees_minor_primary | percent | Percent of trees in plot (10 x 10-m area) dead with secondary branches burned and more than 30 percent of primary branches left |
31 | dead_trees_major_primary | percent | Percent of trees in plot (10 x 10-m area) dead with less than 30 percent of primary branches remaining |
32 | dead_trees_charred_pole | percent | Percent of trees in plot (10 x 10-m area) dead with no primary branches and a charred pole |
33 | root1_ht | cm | Height from current ground level up to first randomly selected adventitious root reported in meters |
34 | root2_ht | cm | Height from current ground level up to second randomly selected adventitious root reported in meters |
35 | root3_ht | cm | Height from current ground level up to third randomly selected adventitious root reported in meters |
36 | root4_ht | cm | Height from current ground level up to fourth randomly selected adventitious root reported in meters |
37 | root5_ht | cm | Height from current ground level up to fourth randomly selected adventitious root reported in meters |
38 | nadircover_shrublive | percent | Percent ground cover composed of live shrubs. |
39 | nadircover_shrubdead | percent | Percent ground cover composed of dead shrubs. |
40 | nadircover_livewoodydebris | percent | Percent ground cover composed live woody debris |
41 | nadircover_woodydebris | percent | Percent ground cover composed of woody debris. |
42 | nadircover_herbaceouslive | percent | Percent ground cover composed of live herbaceous plants. |
43 | nadircover_herbaceousdead | percent | Percent ground cover composed of dead herbaceous plants. |
44 | nadircover_mosslive | percent | Percent ground cover composed of live moss. |
45 | nadircover_mossdead | percent | Percent ground cover composed of dead moss. |
46 | nadircover_liverwortlive | percent | Percent ground cover composed of live liverwort |
47 | nadircover_liverwortdead | percent | Percent ground cover composed of dead liverwort. |
48 | nadircover_mineralsoil | percent | Percent ground cover composed of mineral soil |
49 | nadircover_equisetumlive | percent | Percent ground cover composed of live equisetum |
50 | tree_ht1 | m | Height of tree 1 reported in meters |
51 | tree_condition1 | Condition of tree 1: live or dead | |
52 | tree_ht2 | m | Height of tree 2 reported in meters |
53 | tree_condition2 | Condition of tree 2: live or dead | |
54 | tree_ht3 | m | Height of tree 3 reported in meters |
55 | tree_condition3 | Condition of tree 3: live or dead | |
56 | soil_ph | Soil pH | |
57 | camera_id | Camera name used to photograph the site. This is also the companion folder- filename where a photo would be found. Described in the companion files table at the end of this document section | |
58 | north_photo | North facing photo id number | |
59 | east_photo | East facing photo id number | |
60 | south_photo | South facing photo id number | |
61 | west_photo | West facing photo id number | |
62 | nadir_photo | Nadir facing photo id number | |
63 | nadir_seedling_photo | Nadir seedling photo | |
64 | notes | Additional comments |
Vegetation Biophysical Data:
This file provides vegetation community biophysical data collected 27 locations in eight wildfire areas in July and August of 2016. Data not provided are reported as not_provided.
Table 6. File: NWT_wildfires_biophysical_2016.csv
Column # | Variable | Unit | Description |
---|---|---|---|
1 | site | Unique name given to a field site. The initial alphanumeric code indicates site and fire number and the second part of the name is a site code designated by the research team | |
2 | plot | Plot number within site | |
3 | plot_Size | Size of sampling plot reported in meters by meters | |
4 | date | YYYY-MM-DD | Sampling date |
5 | observer | text | Initials of person(s) who collected the information |
6 | latitude | decimal degrees | Latitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner |
7 | longitude | decimal degrees | Longitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner |
8 | time | HH:MM | Time that data collection at that location began in local time MDT (UTC-6) |
9 | live_canopy_cover | percent | Percent of canopy (tree) cover classified as live |
10 | dominant_cover | Description of the dominant cover type. Choices included: forested; shrub; herbaceous or some combination of these cover types | |
11 | ecosystem | Ecosystem type(s) represented in the plot: bog; fen; lowland; upland see table for defining characteristics | |
12 | medium_shrub_cover | percent | Percent of medium shrubs present |
13 | ground_wetness | Description of the soil moisture status: dry, moist, soggy, standing water, or some combination of these conditions | |
14 | soil_top_moss_condition | Notes on the condition of the top layer of organic soil (moss) with respect to burning: ash, burned, singed, charred, or unburned | |
15 | soil_live_moss_thickness | cm | Thickness of the live moss component of the organic soil layer reported in centimeters |
16 | soil_dead_moss_layer_thickness | cm | Thickness of the dead moss component of the organic soil layer reported in centimeters |
17 | soil_upper_duff_layer_thickness | cm | Thickness of the upper duff component of the organic soil layer reported in centimeters |
18 | soil_lower_duff_layer_thickness | cm | Thickness of the lower duff component of the organic soil layer reported in centimeters |
19 | total_peat_depth | cm | Depth of entire peat layer calculated as the sum of the previous 4 columns reported in centimeters from surface |
20 | low_shrubs_coverage | percent | Percent of ground covered in low shrubs reported as percent of total plot area |
21 | low_shrubs_distribution | Pattern of distribution of low shrubs: reported as E (even), P (peripheral), or patchy | |
22 | woody_debris_coverage | percent | Percent of ground covered in woody debris reported as percent of total plot area |
23 | woody_debris_distribution | Pattern of distribution of low shrubs: reported as E (even), P (peripheral), or patchy | |
24 | sphag_coverage | percent | Percent of ground covered in Sphagnum moss reported as percent of total plot area |
25 | sphag_distribution | Pattern of distribution of Sphagnum moss: reported as E (even), P (peripheral), or patchy | |
26 | reindeer_lichen_coverage | percent | Percent of ground covered in reindeer lichen reported as percent of total plot area |
27 | reindeer_lichen_distribution | Pattern of distribution of reindeer lichen: reported as E (even), P (peripheral), or patchy | |
28 | grasses_coverage | percent | Percent of ground covered in grasses reported as percent of total plot area |
29 | grasses_distribution | Pattern of distribution of grasses: reported as E (even), P (peripheral), or patchy | |
30 | herbaceous_coverage | percent | Percent of ground covered in herbaceous plants reported as percent of total plot area |
31 | herbaceous_distribution | Pattern of distribution of herbaceous plants: reported as E (even), P (peripheral), or patchy | |
32 | feather_moss_coverage | percent | Percent of ground cover that was feather moss |
33 | feather_moss_coverage_distribution | Pattern of distribution of feather moss | |
34 | other_lichen_coverage | percent | percent |
35 | other_lichen_coverage_distribution | Pattern of distribution of lichens | |
36-47 | othertype_groundcoverX | Description of other ground cover types. There are four additional “other” ground cover types. Each ground cover type is followed by the columns othertype_groundcoverX_coverage and othertype_groundcoverX_distribution where X is 1, 2, 3, or 4. See the descriptions below | |
36-47 | othertype_groundcoverX_coverage | percent | Percent of ground covered in other ground cover reported as percent of total plot areas. There are four additional “other” ground covers with the one variable described above and below |
36-47 | othertype_groundcoverX_distribution | Pattern of distribution of other ground cover: reported as E (even), P (peripheral), or patchy. There are four additional “other” ground covers with the two variables described above |
Seedling and Sprouting Data:
This file provides observations of vegetation seedling/saplings and sprouting of mosses and lichen collected from 27 locations in eight wildfire areas in July and August of 2016. Missing or data not reported are provided as -9999 or not_provided.
Table 7. File: NWT_wildfires_seeedling_sprouting_2016.csv
Column # | Variable | Unit | Description |
---|---|---|---|
1 | site | Unique name given to a field site. The initial alphanumeric code indicates site and fire number and the second part of the name is a site code designated by the research team. | |
2 | plot | Plot number within the site; there are up to 6 plots per site | |
3 | date | YYYY-MM-DD | Sampling date |
4 | observers | Initials of person(s) who collected data | |
5 | plot_size | m | Plot sizes as meter x meter |
6 | species | Scientific name of vegetation species measured | |
7 | veg_stage | Growth stage of vegetation: seedling or sprouting | |
8 | number | Number of seedlings or sproutings recorded | |
9 | seedbed | Seedbed type: sphagnum, unburned organic material (duff and litter), thick burned organic material, thin burned organic material, or exposed mineral soil | |
10 | percent_cover | percent |
Percent ground cover composed of species in plot. Percent cover used in cases where unable to count such as moss or lichens. |
Plot Vegetation Inventory Data
This file provides site/plot observations, species inventory, diameter, and height data collected from eight wildfire areas and 27 sites in July and August of 2016. Data not provided or missing are reported as -9999.
Table 8. File: NWT_wildfires_inventory_2015.csv
Column # | Variable | Unit | Description |
---|---|---|---|
1 | site | Unique name given to a field site. The initial alphanumeric code indicates site and fire number and the second part of the name is a site code designated by the research team. | |
2 | plot | Plot number. Each site had up to six plots | |
3 | date | YYYY-MM-DD | Sampling date |
4 | observer | Initials of person(s) who collected the information | |
5 | plot_size | m x m | Size of sampling plot reported as meters by meters |
6 | life_form | Life form: shrub or tree | |
7 | condition | Stem condition either standing or fallen | |
8 | species | Scientific name of stem measured | |
9 | basal_diameter | cm | Basal diameter measured at ground level |
10 | DBH | cm | Diameter at Breast Height (DBH) reported in centimeters measured at 1.3-meters above the ground |
11 | height | m | Height of stem reported in meters |
12 | status | Alive or dead |
Soil Moisture and Temperature Data:
There are two files for soil data collected from the same 11 wildfire areas in July and August of 2016. One file provides measurements made with a Hydrosense I instrument, and the second file provides measurements made with a Hydrosense II. The same variables are provided in both files. The probe period and %VWC were collected at two to six points within each plot.
Data not provided or missing are reported as -9999.
Table 9. Data files: NWT_soil_moisture_hydrosense_1_2016.csv and NWT_soil_moisture_hydrosense_2_2016.csv
Column # | Variable | Units/format | Description |
---|---|---|---|
1 | site | Unique name given to a field site | |
2 | date | YYYY-MM-DD | Date of measurements |
3 | start_time | HH:min | Time of measurements |
4 | observers | Initials of person(s) who collected data | |
5 | probe_depth | Depth of probe | |
6 | soil_ temp_1 | Soil temperature measurement | |
7 | plot_1_period | ||
8 | vmc_plot_1 | % | Percent volumetric moisture content |
9 | soil_temp_2 | Soil temperature measurement | |
10 | plot_2_period | ||
11 | vmc_plot_2 | % | Percent volumetric moisture content |
12 | soil_temp_3 | Soil temperature measurement | |
13 | plot_3_period | ||
14 | vmc_plot_3 | % | Percent volumetric moisture content |
15 | soil_temp_4 | Soil temperature measurement | |
16 | plot_4_period | ||
17 | vmc_plot_4 | % | Percent volumetric moisture content |
18 | soil_temp_5 | Soil temperature measurement | |
19 | plot_5_period | ||
20 | vmc_plot_5 | % | Percent volumetric moisture content |
21 | soil_temp_6 | Soil temperature measurement | |
22 | plot_6_period | ||
23 | vmc_plot_6 | % | Percent volumetric moisture content |
Vegetation Community Characterization Data:
Measurements were collected from six wildfire areas. Data not provided or not reported are recorded as -9999 or as not_provided.
Table 10. File: NWT_wildfires_fieldvalidation_2016.csv
Column # | Variable Name | Unit | Description |
---|---|---|---|
1 | site | Unique name given to a field point | |
2 | date | YYYYMMDD | Sampling date |
3 | time | HH:MM | Time at which field work began in local time (MDT) |
4 | latitude | decimal degrees | Latitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner |
5 | longitude | decimal degrees | Longitude of plot. Coordinates were taken with a handheld GPS unit in a plot corner |
6 | observers | Text | Initials of person(s) who collected data |
7 | thaw_depth | cm | Depth of soil to frozen ground layer reported in centimeters. Measurements were made from the top of the ground cover at the 37 unburned sites. |
8 | peat_depth | cm | Depth of organic peat soil reported in centimeters |
9 | soil_pH | pH units | |
10 | ecosystem | Type of ecosystem, individually or in combination; Bog/Bog Like, Fen/Fen Like, Treed Bog, Shrub Fen, Treed Fen, Open Fen, Upland, Marsh, Shrubby, Sparse Trees, Lowland White Pine | |
11 | ground_wetness | Wetness of ground: Dry (no moisture present), Moist (moisture present but not saturated), Soggy (saturated with water but no areas of standing water), or Standing Water (visible standing water present in plot) | |
12 | vegetation | List of vegetation species present | |
13 | dense_trees | percent | Percent of plot covered in dense trees. Plot areas were 0.5 acre |
14 | dense_trees_dist | Description of dense tree distribution: E (evenly distributed), C (center only), and P (peripheral) | |
15 | moderate_trees | percent | Percent of plot covered in moderate trees. Plot areas were 0.5 acre |
16 | moderate_trees_dist | Description of moderate tree distribution: E (evenly distributed), C (center only), and P (peripheral) | |
17 | sparse_trees | percent | Percent of plot covered in sparse trees. Plot areas were 0.5 acre |
18 | sparse_trees_dist | Description of sparse tree distribution: E (evenly distributed), C (center only), and P (peripheral) | |
19 | open_water | percent | Percent of plot covered in open water. Plot areas were 0.5 acre |
20 | open_water_dist | Description of open water distribution: E (evenly distributed), C (center only), and P (peripheral) | |
21 | shrubby | percent | Percent of plot covered in shrubs. Plot areas were 0.5 acre |
22 | shrubby_dist | Description of shrub distribution: E (evenly distributed), C (center only), and P (peripheral) | |
23 | moss | percent | Percent of plot covered in moss. Plot areas were 0.5 acre |
24 | moss_dist | Description of moss distribution: E (evenly distributed), C (center only), and P (peripheral) | |
25 | grass_sedge | percent | Percent of plot covered in grass/sedge. Plot areas were 0.5 acre |
26 | grass_sedge_dist | Description of grass/sedge distribution: E (evenly distributed), C (center only), and P (peripheral) | |
27 | herbaceous_cover | percent | Herbaceous cover |
28 | herbaceous_cover_dist | Distribution of herbaceous cover | |
29 | other_descrip | Description of other types of ground cover | |
30 | other | percent | Percent of plot covered in other vegetation. Plot area is 0.5 acre |
31 | other_dist | Description of other vegetation distribution: E (evenly distributed), C (center only), and P (peripheral) | |
32 | spp1 | genus_species | Scientific name of dominant species ( grasses and sedges not identified to species) |
33 | spp1_live_ht | m | Average height of live dominant species 1 |
34 | spp1_dead_ht | m | Average height of dead dominant species 1 |
35 | spp1_density | percent | Percent of area covered by dominant species 1 |
36 | spp1_live | percent | Percent of dominant species 1 live (by area) |
37 | spp1_dead | percent | Percent of dominant species 1 dead (by area) |
38 | spp1_stage | Growth Stage for dominant species: dormant, emerging, seedling, immature, mature, flowering | |
39 | spp2 | genus_species | Scientific name of dominant species ( grasses and sedges not identified to species) |
40 | spp2_live_ht | m | Average height of live dominant species 2 |
41 | spp2_dead_ht | m | Average height of dead dominant species 2 |
42 | spp2_density | percent | Percent of area covered by dominant species 2 |
43 | spp2_live | percent | Percent of dominant species 2 live (by area) |
44 | spp2_dead | percent | Percent of dominant species 2 dead (by area) |
45 | spp2_stage | Growth Stage for dominant species: dormant, emerging, seedling, immature, mature, flowering | |
46 | ht_lowest_living_branch | m | Height of average lowest living branch reported in meters |
47 | soil_live_moss | cm | Depth of live moss layer present in 40-cm soil profile |
48 | soil_dead_moss | cm | Depth of dead moss layer present in 40-cm soil profile |
49 | soil_upper_duff | cm | Depth of upper duff layer present in 40-cm soil profile |
50 | soil_ lower_duff | cm | Depth of lower duff layer present in 40-cm soil profile |
51 and columns 53, 55, 57, 59, 61, 63 | sample_x_depth | Depth of sample for seven samples where X=sample1 to sample 7 | |
52, and columns 54, 56, 58, 60, 62, 64 | sample_x_horizon | Sample horizon for seven samples where X=sample1 to sample 7 | |
65 | camera_id | Camera name used to photograph the site- this is also the companion file name where a photo would be found. Described in the companion files table at the end of this document section | |
66 | north_photo | North facing photo id number | North facing photo id number |
67 | east_photo | East facing photo id number | East facing photo id number |
68 | south_photo | South facing photo id number | South facing photo id number |
69 | west_photo | West facing photo id number | West facing photo id number |
70 | nadir_photo | Nadir facing photo id number | Nadir facing photo id number |
71 | other_photos | Additional photos | |
72 | notes | Comments |
Companion Files
File name | Description |
---|---|
1326_photos.zip |
Compressed directory containing photos (in .jpg format) numbered 2910-3385 showing study areas in the data file NWT_Wildfires_burn_severity_2016.csv. The photos are noted as a number and by the camera used to take the photos (camera_id 1326) in the data file. For each photo, there is also the same photo stamped with the latitude and longitude (_tag.jpg), two map files for the site (_Map1 and _Map2.jpg), and a thumbnail image of the photo (_thm.jpg). This zip file also contains a pdf named 1326_temp_tag-Standard.pdf which provides a compilation of all of the images and map files just described, and the file 1326_geo.kml for viewing the photos in Google Earth. |
1326_geo.zip | A compressed shapefile of point features (1326_geo.shp) that provides metadata about the photographs in 1326_photos.zip: location, elevation, photo direction, timestamp, and camera model |
1326_geo_FOV.zip | A compressed shapefile of polygon features (1326_geo_FOV.shp) that depict the fields of view of the photographs in 1326_photos.zip |
1327_photos.zip |
Additional photos (*.jpg format) taken of the study sites not included in the data files. For each photo, there is also the same photo stamped with the latitude and longitude (_tag.jpg), two map files for the site (_Map1 and _Map2.jpg), and a thumbnail image of the photo (_thm.jpg). This zip file also contains a pdf named 1327_temp_tag-Standard.pdf which provides a compilation of all of the images and map files just described, and the file 1327_geo.kml for viewing the photos in Google Earth |
1327_geo.zip | A shapefile of point features (1327_geo.shp) that provides metadata about the photographs in 1327_photos.zip: location, elevation, photo direction, timestamp, and camera model |
1327_geo_FOV.zip | A shapefile of polygon features (1327_geo_FOV.shp) that depict the fields of view of the photographs in 1327_photos.zip |
2015_NWT_fireprogression.kmz | The shapefile 2015_NWT_fireprogression.shp provided in .kmz format for visualization in Google Earth |
Wildfires_2014_NWT_Canada.pdf | This guide document in pdf format |
Application and Derivation
The goal was to identify and collect remote sensing and field data to support the science necessary to investigate the impacts and consequences of the 2014 and 2015 fires in Northwest Territories.
Quality Assessment
Data Acquisition, Materials, and Methods
Study areas
This project used remote sensing and field data to characterize the impacts of wildfires that occurred in 2014 and 2015 in the North Slave, South Slave, and Dehcho Regions of Northwest Territories, Canada. The ABoVE Project grid locations of these study areas are Ah2v1.Bh0v5, Ah2v1.Bh1v4, Ah2v1.Bh1v5, Ah2v1.Bh2v5, and Ah2v2.Bh0v0. For additional information, refer to the ABoVE Grid Reference: https://above.maps.arcgis.com/home/item.html?id=ad3dc7c0ecef41bb8e2d928ce2ed7a48
The focus area of this study focuses on four 2014 NWT fires (ZF17, ZF20, SS3,SS15) and five 2015 NWT Fires (ZF14, ZF2, SS50, SS81, SS28).
Figure 2. Wildfire areas with burned and validation field site locations in the Northwest Territories.
Validation areas
A total of 13 field locations at six wildfire areas were sampled in NWT, Canada as validation sites. None of the validation sites were burned but the sites were taken to train and validate the pre-burn peatland type map. Data collection followed a standardized protocol. Field crews used a hand held GPS, a GPS camera, maps of aerial photographs, and tape measures. At each location, a vegetative index was constructed, ecosystem type was assigned, species diversity noted, dominant species composition assigned, water level measured, vegetation life stage recorded, and height and density measured for the overstory. Thaw depth was measured with a peat rod from the top of the moss to the frozen layer. Additionally, hand drawn maps and delineation of laminated aerial photograph maps distinguished unique vegetation types and species transition areas. Geolocated photographs were taken in the four cardinal directions at a centralized location providing an additional layer of validation and ground truth for each location.
Fire Progression Maps
A fire progression algorithm was used that enabled an assessment of wildfire progression rates at a daily time scale. This algorithm was developed as a semi-automated approach suitable for developing daily estimates of area burned from satellite observations of fire occurrence. Fire progression was based on observed active fire detections from both the Terra and Aqua satellites using the MODIS active fire product (MCD14ML; Giglio et al., 2003). Fire progression was assessed at a daily time step and was based on the first observation of fire occurrence in a particular MODIS 1-km pixel within a burn scar. The algorithm was focused on modeling the approximate date of burning within the combined burned area product using the date/time information contained in the MODIS active fire product and adjusted for the local standard time correction.
Active fire detections were first processed using the Fire Spread Reconstruction (FSR) approach, which clusters individual fire points in space-time to identify contiguous fire events and groups of fire events creating a single burn scar (Loboda and Csiszar 2007). The clustered fire events were subsequently processed to separate the first date of fire detection within a specific MODIS pixel from subsequent detections, wherein the pixel continues to emit a sufficient amount of thermal energy to warrant the detection of on-going burning. The date of burning between adjacent dates of fire detections in fire progression surfaces was interpolated using the inverse distance mapping algorithm with a radius of 3 km.
Field Data (refer to Table 4 for a listing of the sites)
Biophysical site characteristics, burn severity, soil moisture, thaw depth, and seedling/sapling data were collected in up to six plots along two transects representing a homogenous area of 100 x 100-m.
Burn Severity
Burn severity was measured at 27 locations in eight wildfire areas. A 10 sq m plot was created using reel tape. Burn damage severity class was recorded for moss, litter, shrub and canopy. Nadir percent cover by vegetation class was recorded for live/dead shrubs, woody debris, herbaceous, and moss. Three representative tree heights were recorded and up to five adventitious root heights were recorded. Peatland type, thaw depth, and peat thickness as well as ash presence are also reported for all plots.
Figure 3. Photo of a burned site (fire SS3) near Kakisa.
Biophysical Characteristics
Field surveys were conducted at eight wildfire areas. The data file provides peatland type, wetness, thaw depth, soil organic layer thicknesses and the type of ground cover present as well as area covered by each ground cover type. Plot size varied from 1 sq m to 10 sq m.
Soil Moisture
Soil moisture data were collected at 11 wildfire areas with Hydrosense 1 and Hydrosense II instruments at the same 40 sites (refer to Table 4 for a listing of the sites). Five measurements were made at each depth for each plot.
Temperature was measured using a Hannah Instruments HI 145 probe. Two different lengths of probes were used: 20 cm and 12 cm. Both probes were placed straight down into the soil. In addition, at 6 cm depth, the 12 cm probe was placed at a 30- degree angle. The probe period and %VMC were collected at six points within each plot. For validation of remote sensing data, the moisture data were collected during Radarsat-2 overpasses.
Seedling/Sprouting
A total of eight wildfire areas were sampled. Plots of either 1 sq m or 0.5 sq m were set up in the corner of each site, where all seedling and sprouting vegetation was recorded along with the ground cover type.
Inventory-Aboveground Biomass
A total of 11 areas were sampled. At each site a plot was taped off (varying in size between 1 to 10 sq m) and each standing tree/shrub was measured. The tree/shrub species and DBH or basal diameter was recorded along with the height of representative trees.
Data Access
These data are available through the Oak Ridge National Laboratory (ORNL) Distributed Active Archive Center (DAAC).
ABoVE: Burn Severity, Fire Progression, and Field Data, NWT, Canada, 2015-2016
Contact for Data Center Access Information:
- E-mail: uso@daac.ornl.gov
- Telephone: +1 (865) 241-3952
References
Giglio, L., Descloitres, J., Justice, C.O., and Y.J. Kaufman (2003) “An Enhanced Contextual Fire Detection Algorithm for MODIS.” Remote Sensing of Environment 87, no. 2-3, 276-282. https://doi.org/10.1016/S0034-4257(03)00184-6
Loboda TV, Csiszar IA (2007) Reconstruction of fire spread within wildland fire events in Northern Eurasia from the MODIS active fire product. Global and Planetary Change 56, 258–273. https://doi.org/10.1016/j.gloplacha.2006.07.015