Background: I have received a lot of feedback on LANDFIRE-assigned fire behavior fuel models (mainly FBFM40) being incorrect in certain areas, especially in terms of unnatural fuels such as agriculture (see below). What I have learned is when investigating a discrepancy in fuel model, there are three major lines of investigation:
1. Input data: Are other LANDFIRE datasets that contribute to fuel model assignment accurately represented? This mainly includes existing vegetation type, cover, height, and disturbance.
2. Rule sets: Are the rule sets based on combinations of EVT, EVH, EVC, and disturbance accurate? You can view the rule sets for assigning fuel models based on these factors in a database or through working with the LANDFIRE Total Fuel Change Tool.
3. Assumptions and conditions: If other supporting datasets accurately represent the landscape, review the ‘assumed’ environmental conditions used for FBFM mapping and average fuel properties driving the models, as explained in Reeves et al., 2009, quoted below:
o “The ‘assumed’ environmental conditions used for the FBFM mapping process are those that typify the fire weather normally encountered during the peak of the burning season in the geographic region being evaluated.”
o “Both surface fire behavior fuel model (FBFM) classifications mapped by the LANDFIRE Project represent average fuel properties needed to drive the surface fire spread model created by Rothermel (1972, 1983). These properties include fuel load by category (live and dead) and size class (0 to 0.64 cm (0 to 0.25 in) 0.64 to 2.54 cm (0.25 to 1.0 in) and 2.54 to 7.62 cm (1.0 to 3.0 in) diameter), surface-area-to-volume ratio of each size class, heat content by category, fuel bed depth, and moisture of extinction (i.e. the moisture limit beyond which fire cannot spread) (Scott and Burgan 2005). These surface FBFMs enable estimates of expected fire behavior under specific moisture conditions (Burgan and Rothermel 1984).”
What we can do: In order for LANDFIRE to make changes to any of their datasets, models, or rulesets, a general trend or widespread issue needs to be identified and described. This is because LANDFIRE is mapping many complex relationships throughout the entire United States, and cannot incorporate all local-level phenomena. The fire behavior fuel model (FBFM 13 and 40) rulesets are unique for each map zone, and therefore changes need to be relevant at that level of geography. I have proposed collecting detailed information on prescribed and wild fires to address the three lines of investigation above and document this properly for myself, all of you, and the LANDFIRE mappers to start to understand trends on a broader scale (see working draft below). In addition, there is the potential to incorporate a version of Provisional Modeling Dynamic Fuels with an Index System (MoD-FIS) in the Northeast if we can identify the main factor(s) driving changes in fuels. In the Southwest it was level of herbaceous cover, so MoD-FIS in that region incorporates seasonal variability in herbaceous cover. In the Southeast, drought was determined to be the main factor driving changes in fuels. Therefore, LANDFIRE created drought-based fuel dynamic fuel model datasets for that region. If we can demonstrate the need for a similar product, we may just get it! I am working with the LANDFIRE mappers to develop a table to capture the information they would need to make a determination like this. You will hear from me soon on how to provide information for that table.
Draft table fields: