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Page Title - Frequently Asked Questions

What is the Monitoring Trends in Burn Severity (MTBS) project?

MTBS is a multi-year national project to map the location, extent and associated burn severity of all large fires (including wildfire, resource benefit fire (WFU), and prescribed fire) in the United States across all ownerships from 1984 and beyond.

Why was the MTBS project implemented?

In 2004, the Wildland Fire Leadership Council adopted a strategy to monitor the effectiveness and effects of the National Fire Plan and the Healthy Forests Restoration Act (HFRA) initiated in 2000 and 2002, respectively. Module 2.1 of this strategy identifies the need to assess the environmental impacts of large wildland fires and identify trends in burn severity on all lands across the United States. This requires a consistent information base to synoptically assess environmental impacts and trends. Consequently, the MTBS project was implemented to generate and summarize burn severity information for this national analysis of trends in fire severity. Additionally, the project meets the recommendations outlined by a 2004 Government Accountability Office (GAO) report specifying the need for providing geospatial fire and burn severity characterization data at regional and sub-regional scales to support resource and risk assessments, resource management, monitoring, and research activities.

What is the Wildland Fire Leadership Council (WFLC)?

The Wildland Fire Leadership Council (WFLC) is a National level, interagency body with the responsibility to implement and coordinate the National Fire Plan (NFP) and other federal wildfire management policies. WFLC is the primary sponsor of the MTBS project.

Who is responsible for producing MTBS geospatial data and products?

The Monitoring Trends in Burn Severity project is implemented jointly by the U.S. Geological Survey (USGS) Center for Earth Resources Observation and Science (EROS) and the U.S. Department of Agriculture Forest Service, Remote Sensing Applications Center (RSAC). MTBS production work is divided between the two centers. Selected individuals from the Forest Service and DOI agencies, academia and NGOs provide technical consultation and support.

Who provides project funding for MTBS?

Funding support for the project is divided between the Forest Service and the Department of Interior.

How is MTBS related to LANDFIRE?

Starting in 2008, the LANDFIRE program began updating their existing vegetation and fuel layers to reflect landscape changes that had occurred since the nominal date (2001) of the baseline LANDFIRE dataset. MTBS provides LANDFIRE with a comprehensive and consistent source of fire disturbance and characterization data for fires that meet the MTBS size threshold. These data are used by LANDFIRE to update specific layers to reflect current conditions.

What is the difference between MTBS and BAER?

Similar to the MTBS project, Burned Area Emergency Response (BAER) Imagery Support is a cooperative effort between the USDA Forest Service Remote Sensing Applications Center and the USGS Earth Observation and Science Data Center. Through their combined efforts, the centers provide rapid response post-fire satellite imagery and emergency assessments of vegetation burn severity. A summary document describes the purpose and objectives of the BAER Imagery Support program and its relationship to the MTBS project.

Why does the MTBS data record begin in 1984?

MTBS leverages Landsat (TM/ETM+/OLI) satellite data for mapping and characterizing fires. Although the Landsat mission extends back to 1972, the first Thematic Mapper sensor was launched on Landsat 4 in 1982. Consequently, Landsat Thematic Mapper data continuity extends back to 1984.

What is burn severity?

In the MTBS project, "burn severity" refers specifically to fire effects on above-ground biomass. The definition is drawn from the reference: NWCG Glossary of Wildland Fire Terms and is based on the term Fire Severity, which is defined as: "Degree to which a site has been altered or disrupted by fire; loosely, a product of fire intensity and residence time."

The following additional statements further clarify the nature of the products developed by this project:
  • Burn severity is a composite of first-order effects and second order effects that arise within one growing season.
  • Burn severity relates principally to visible changes in living and non-living biomass, fire byproducts (scorch, char, ash), and soil exposure.
  • Burn severity occurs on a gradient or ordinal scale.
  • Burn severity is a mosaic of effects that occur within a fire perimeter.
  • Longer term effects are controlled by variables that evolve after a fire and are beyond the scope of this project.
  • Burn severity is mappable and remotely sensed data provide a measurement framework.

What is NBR?

The Normalized Burn Ratio (NBR) is a normalized index that emphasizes the spectral response of fire-affected vegetation by leveraging Landsat near infrared and short-wave infrared bands in an effort to provide the best contrast between photosynthetically healthy and burned vegetation.

What is dNBR?

The differenced Normalized Burn Ratio (dNBR) is a differenced NBR image, or change image, created where the post-fire NBR is subtracted from the pre-fire NBR. The dNBR may be used to discriminate burned from unburned areas and estimate vegetation burn severity classes.

How does MTBS know where the fires are located for mapping?

MTBS utilizes existing wildfire and prescribed fire occurrence data collected from state and federal agencies/organizations. Fire occurrence databases with reasonably precise geospatial descriptions (latitude/longitude, legal description, etc.) are compiled and standardized to generate a point location dataset. Core database elements are compiled as a part of this dataset include, but are not limited to, the fire incident ID and name, fire type, reported fire size, date of fire ignition, date of fire containment, date of fire declared out. The MTBS project uses this dataset to support all phases of the fire mapping process (i.e. to determine the appropriate assessment strategy, selection of appropriate satellite image data, association of the fire information with the appropriate burn area identified using remote sensing data, etc.).

What size of fires does MTBS map?

In the western continental United States, Alaska, and Hawaii, MTBS inventories and maps all "mappable" fires >= 1,000 acres. For the eastern continental United States and Puerto Rico, "mappable" fires >= 500 acres in size are inventoried and mapped.

What is a "mappable" fire?

The following conditions are required to identify and accurately map a fire using Landsat imagery:
  1. Accurate fire location coordinates that can be matched to a burn scar visible on imagery
  2. Accurate fire size information is necessary to ensure that fires meeting the MTBS size criteria are properly included (e.g. a 50 acre fire reported as 5,000 generally will not be mapped except as noted below. Conversely, a 5,000 acre fire may be missed if it is reported as 50 acres).
  3. Accurate date of ignition and out date so appropriate dates of imagery can be acquired for mapping, particularly for initial assessments.
  4. Cloud free observation on both pre-fire and post-fire imagery, as per prescribed assessment strategy, to avoid obscuration of the fire area.
  5. Fires of very low severity may not be visible in the imagery and thus not possible to delineate or characterize.

Why are some small fires found in the database?

There are three instances where fires smaller than the stated size thresholds for the western United States (1,000 acres) and eastern United States (500 acres) may be present in the MTBS database. First, fires are targeted for mapping by the MTBS project based upon their reported size in fire occurrence databases provided by various federal, state and other sources. Errors in reported fire size in these source databases may result in fires significantly smaller than the stated thresholds being targeted and mapped. Second, as a result of a separate agreement between the USGS and National Park Service, the USGS conducts burn severity mapping for any fire requested by the National Park Service. Consequently, these fires may be less than the stated MTBS size thresholds. Since the USGS maps these fires according to the MTBS mapping protocol, they are included as part of the MTBS database. Lastly, other fires in the source fire occurrence databases may have met the stated MTBS size threshold; however, their size, based on remote sensing analysis, is below the threshold.

What is a revised fire?

A "revised" fire is a modified version of the original geospatial data and mapping products for a mapped MTBS fire. If a need for correction to the original dataset is identified through the MTBS quality control process, the geospatial data and mapping products are revised accordingly and republished. The original MTBS dataset is removed from the data distribution archive.

What do Initial Assessment and Extended Assessment mean?

Each fire that is mapped by MTBS has either an "Initial" or "Extended" assessment strategy. An Initial Assessment relies on post-fire satellite data typically acquired at the first opportunity after the fire in order to capitalize on the maximum postfire data signal and is used primarily in ecosystems that exhibit rapid post fire vegetation response (i.e. grass, herbaceous and particular shrubland systems). An Extended Assessment relies on post-fire satellite data typically acquired during the growing season following a fire in order to include any delayed first order fire effects (e.g. initial site response and early secondary effects).

How were the particular MTBS fire size thresholds determined?

When the MTBS project began, focus was on the period between 1984 and 2010. Fires that occurred, regardless of size, in the United States during that period, numbers in the several hundreds of thousands. Unfortunately, due to resource constraints and technical limitations, the MTBS project could not, and cannot map every fire that has occurred. Consequently, during the planning stages of the MTBS project, analysis of available wildfire occurrence data determined that the proposed size thresholds (>= 500 acres in the eastern United States and >= 1,000 acres in the western United States) would map <5% of the total number of fires during the 1984 to 2010 period, but account for approximately 95% of the total area burned. These size specifications provide MTBS the ability to meet the monitoring requirements set forth by WFLC and the GAO within a reasonable cost and timeframe.

What kind of fires does MTBS map?

MTBS maps all wildfires, resource benefit fires (WFUs), and prescribed fires identified using reliable fire occurrence information.

What is the citation for MTBS data and reporting products?

Citation Target Reference Example
General information from MTBS project website Webpage Title. (revision date). MTBS Project Homepage. Available online: URL [Access Date]. Monitoring Trends in Burn Severity. (2009, November - last revised). [MTBS Project Homepage, USDA Forest Service/U.S. Geological Survey]. Available online:
http://mtbs.gov/index.html [2009, December 12].
MTBS geospatial datasets Webpage Title: Data product. (revision date). Agencies. Available online: URL [Access Date]. MTBS Data Access: Fire Level Geospatial Data. (2009, November - last revised). MTBS Project (USDA Forest Service/U.S. Geological Survey). Available online:
http://mtbs.gov/dataquery/individualfiredata.html [2009, December 12].
MTBS project reports Report compiler. Publication date. Report title. Available online: URL. Schwind, B. (compiler). 2008. Monitoring Trends in Burn Severity: Report on the PNW & PSW Fires—1984 to 2005. Available online: http://mtbs.gov/.

What datasets are compiled by MTBS for each fire?

The following geospatial datasets and mapping products are produced for every MTBS fire. File format is noted in parentheses.
  • Pre-fire Landsat 30m reflectance image subset (GeoTiff)
  • Post-fire Landsat 30m reflectance image subset (GeoTiff)
  • 30m dNBR image subset (GeoTiff)
  • 30m RdNBR image subset (GeoTiff)
  • 30m 6-class thematic burn severity (GeoTiff)
  • Burned area perimeter (ESRI shapefile)
  • Non-processing area mask (ESRI shapefile)
  • FGDC metadata (text/XML)
  • Page-sized burn post-fire Landsat image and burn severity map with burn severity statistical summary (PDF)
  • Google Earth map with pre/post Landsat image, burn scar boundary and thematic burn severity data (KMZ)
  • Statistical summary of burn severity by key GIS layers (dbf)
  • Fire table containing key fire occurrence attributes (dbf)

Does the MTBS project provide mosaicked geospatial products?

Yes. Currently, three MTBS datasets are provided as seamless national data products. MTBS burn area boundary polygons and fire occurrence points are each provided as a single nationwide dataset that includes the continental United States, Alaska, Hawaii and Puerto Rico. Thematic burn severity data are also mosaicked to generate annual, seamless burn severity raster layers created individually for the continental United States, Alaska, Hawaii and Puerto Rico. All three of these national datasets can be downloaded from the MTBS National Geospatial Data webpage.

What is the spatial resolution/scale of MTBS data?

All MTBS raster datasets are generated from Landsat (TM/ETM+/OLI) image data which is acquired at a spatial resolution of 30 meters. MTBS vector datasets (burn scar boundaries) are delineated from imagery and burn severity index data at a map scale of 1:24,000 to 1:50,000.

What is the projection/coordinate system of MTBS data?

All MTBS data are provided in Albers Equal Area projection using the regional projection parameters specified below for the continental United States, Alaska, Hawaii and Puerto Rico. User note: the positional accuracy difference between NAD83 and WGS84 is negligible given the resolution/scale of MTBS data.

Projection Parameter CONUS Alaska Hawaii Puerto Rico
Projection Albers Equal Area Albers Equal Area Albers Equal Area Albers Equal Area
Spheroid GRS 1980 WGS 84 WGS 84 GRS 1980
Datum NAD83 WGS 84 WGS 84 NAD83
Latitude of 1st standard parallel 29:30:00 N 55:00:00 N 8:00:00 N 8:00:00 N
Latitude of 2nd standard parallel 45:30:00 N 65:00:00 N 18:00:00 N 18:00:00 N
Longitude of central meridian 96:00:00 W 154:00:00 W 157:00:00 W 66:30:00 W
Latitude of origin of projection 23:00:00 N 50:00:00 N 3:00:00 N 3:00:00 N
False easting of central meridian 0 meters 0 meters 0 meters 0 meters
False northing at origin 0 meters 0 meters 0 meters 0 meters

How does MTBS determine the thematic burn severity classes?

Thresholding continuous burn severity index data into thematic burn severity classes is a considerable technical procedure and varies slightly between fires in different ecological settings. A technical description of the thresholding process is documented in recent MTBS Project Reports and the paper "A Project for Monitoring Trends in Burn Severity".

Can I customize the burn severity data for my fire(s) of interest?

Yes. For each MTBS fire, the continuous burn severity index, the dNBR, is provided. The continuous burn severity thresholds selected by MTBS to identify the respective thematic burn severity classes are published as part of the metadata. To customize the burn severity thresholds established by MTBS and create a thematic burn severity product more applicable to local resource management needs, users have the option of gathering additional ground-based information and local knowledge, which may result in different thresholds than those established by MTBS.

What is the composite burn index?

The composite burn index, or CBI, is a field-based protocol that estimates the ecological effects of fire on individual strata within a plot or site in a burned area. The composite state of these post-fire conditions are collectively related to the signal detected by moderate resolution satellite data.

Is composite burn index data available for all fires?

No. However, thousands of composite burn index (CBI) plot data have been collected for a number of fires. The MTBS project is coordinating with project collaborators to compile the available CBI plot data into a single database for access by users.

What are the MTBS thematic burn severity data class descriptions?

0 - Background
1 – Unburned to Low
2 – Low severity
3 – Moderate severity
4 – High severity
5 – Increased greenness
6 – Non-processing area

Are MTBS burn area boundaries the same as incident perimeters?

MTBS burn area boundaries are delineated from interpretation of post-fire Landsat reflectance imagery and continuous burn severity indices derived from Landsat. Data and methods used to delineate incident perimeters are highly variable and may include both ground based and airborne/satellite image data. Consequently, MTBS burn area boundaries and incident perimeters may not have complete correspondence. Some examples of how differences can be explained include:
  1. MTBS burn area delineations may not include surface burns that are not visible because they occur under unburned vegetation canopies. These areas may or may not be included in incident perimeters depending ground-based information was available.
  2. MTBS burn area boundaries do not delineate unburned islands within the fire area whereas incident perimeters typically do, at least for larger unburned islands.
  3. Incident perimeters may be delineated to the extent of fire containment lines. Fires may or may not actually extend to containment lines in some cases resulting in overestimates of fire area.

What are the "stripes" that appear on some MTBS thematic burn severity datasets?

These areas are part of the "Non-processing area" class and are data gaps within a Landsat 7 SLC-off reflectance imagery used in the MTBS fire mapping process for that fire. The Landsat 7 SLC-off product is further described by the USGS Landsat Project.

How often is new MTBS data released?

New geospatial fire data and reporting data are released by the project periodically. Users will be notified of new data releases on the "What’s NEW" webpage on the MTBS website. In addition, the date of the latest MTBS data release is noted at the top of the MTBS Data Access webpage.

I have found an MTBS dataset that has a problem. What do I do?

If you discover an issue with any of the MTBS geospatial datasets, please inform the MTBS project at mtbs@fs.fed.us. In the submitted email, please provide the name of the dataset and a short description of the problem. The MTBS project will evaluate the issue, make necessary corrections and repost the revised dataset to the MTBS project website.

How are MTBS geospatial data provided to users?

MTBS geospatial data are provided at two geographic levels: fire-level and national level. The suite of geospatial data compiled for each individually mapped MTBS fire (burn area boundary, continuous burn severity indices, thematic burn severity, etc.) are bundled as a fire-level dataset and provided as a single, compressed archived file. The compressed archive file for each completed MTBS fire can be located for download by using the MTBS Data Search and Distribution Tools.

Selected datasets from the suite of fire-level data are appended together by the MTBS project to create seamless national geospatial datasets. MTBS burn area boundary polygons are appended together as a single nationwide ESRI polygon shapefile with pertinent attributes. Additionally, fire occurrence point locations are calculated for each MTBS fire and compiled into a nationwide ESRI point shapefile. Thematic burn severity data for each individual MTBS fire are also mosaicked to generate annual, seamless burn severity GeoTiff images. All three of these national MTBS datasets can be downloaded from the MTBS National Geospatial Data webpage.

How do I access MTBS geospatial data for a particular fire?

MTBS fires can be searched using the MTBS Data Search and Distribution Tools. These tools allow users to create customized queries using one or more criteria to identify specific MTBS fires of interest. Fires meeting the user-designed query are listed with their associated geospatial datasets and mapping/visualization products that can be downloaded individually or en masse.

I cannot identify a particular fire. Are all fires that meet the MTBS size thresholds mapped?

MTBS attempts to map all large fires based on the best available fire occurrence data and satellite imagery. However, due to one or more particular factors (i.e. erroneous reporting information, satellite imagery of poor quality, etc.), some fires cannot be mapped by the project.

What if I just want mapping products for MTBS fires and not the geospatial data?

In addition to the geospatial datasets, the MTBS project provides ready to use mapping and visualization products for each fire. These products include a letter-sized PDF map depicting the burn scar boundary superimposed on both a post-fire reflectance image and the thematic burn severity data. A location map, mapping summary and burn severity acreage summary are also included in the map product. A compressed Keyhole Markup Language (KML) is also provided for each MTBS fire that can be used in Google Earth. The KML consists of the pre/post fire Landsat image, burn area boundary, thematic burn severity data, and relevant fire mapping information. Both of these products are accessible for each fire using the MTBS Data Search and Distribution Tools.

Can I get statistical summaries of MTBS burn severity data?

Yes. MTBS thematic burn severity data are analyzed using several relevant GIS datasets. Results of these analyses can be queried using the MTBS Reporting Summaries web page to generate tabular and graphical summaries.

What is the source of administrative ownership used in MTBS reporting summaries?

Administrative ownership data used in MTBS reporting summaries utilize federal and state surface management agency geospatial data. These data are compiled by the Bureau of Land Management Land & Resources Project Office as part of the National Integrated Land System (NILS).

What is the source of the land cover data used in MTBS reporting summaries?

Land cover data used in MTBS summaries are based on the following: 1) National Land Cover Database 2001 (NLCD 2001) for the continental United States and Puerto Rico; 2) National Oceanic and Atmospheric Administration (NOAA) Coastal Change and Analysis Program (C-CAP) Land Cover Analysis data for Hawaii; and 3) National Land Cover Database 2001 (NLCD 2001) and Alaska Earth Cover Classification (circa 2000) compiled by the Bureau of Land Management and Ducks Unlimited for Alaska. The Alaska and Hawaii MTBS reporting analysis results are currently being transitioned and updated to be based entirely on the NLCD 2001 database.

I need help understanding MTBS data. Who can I contact?

For technical support regarding MTBS data or if you have a question about any other aspect of the MTBS project, please contact us via email at mtbs@fs.fed.us.

I’m interested in using remote sensing for assessing fire effects and how MTBS utilizes this technology. How can I find out more information?

Technical guidance on Landsat-based remote sensing data processing and analysis, fire severity assessment strategies, and ground based measures of fire effects are documented as part of the Fire Effects Monitoring and Inventory System (FIREMON) in the FIREMON Landscape Assessment – Version 5 document. Additional publications and technical documentation on mapping and characterizing burn severity are provided on the MTBS Scientific References webpage.

What is Landsat?

Landsat is a series of Earth resource satellites jointly managed by NASA and the USGS. The first of eight Landsat missions was launched in 1972 with the latest launch occurring in 2013. Multispectral satellite imagery, collected by the Thematic Mapper (TM) sensor on board the Landsat 4 and 5 missions, the Enhanced Thematic Mapper (ETM+) sensor on board the Landsat 7 mission, and the Operational Land Imager (OLI) sensor on board the Landsat 8 mission, have been or are currently being used for mapping and characterizing MTBS fires. Additional technical information on Landsat is available from the NASA Landsat Program website and the USGS Landsat Missions website.

Why is Landsat used for mapping MTBS fires?

Landsat Thematic Mapper (TM), Landsat Enhanced Thematic Mapper (ETM+), and Landsat Operational Land Imager (OLI) data provide the longest consistent record of relatively high spatial and spectral resolution data for mapping fire severity. Landsat TM/ETM+/OLI data are also cost effective and are available for the entire temporal and geographic extent of the MTBS project.

If you have a question which has not been addressed on the FAQs page, please send us an email.
Your question will be forwarded to the MTBS project and you will receive an answer. If appropriate, your question will be added to the MTBS FAQs web page.

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