Introduction to the Natural Fuels Photo Series

WHAT IS THE NATURAL FUELS PHOTO SERIES?
The first phase of the natural fuels photo series was a collection of six volumes, each representing a region of the United States (Volumes I-VI). Additional phases of the natural fuels photo series included new volumes (Volumes VII-XII) and supplemental volumes (Volumes IIa, Va, and VIa). Volume I included sites in mixed-conifer, western juniper, sagebrush, and grassland ecosystems and volume XI included sites in sagebrush-steppe and old-growth forest suitable for nesting in the Pacific Northwest. Volume II included sites in black and white spruce ecosystems and volume IIa included sites in hardwood ecosystems undergoing succession to spruce in Alaska. Volume III included sites in lodgepole pine, quaking aspen, and gambel oak ecosystems in the Rocky Mountains. Volume IV included sites in pinyon-juniper, sagebrush, and chaparral ecosystems in the Southwest. Volume V included sites in red and white pine, northern tallgrass prairie, and mixed oak ecosystems, and volume Va included sites in jack pine ecosystems in the Midwest. Volume VI included sites in longleaf pine, pocosin, and marsh grass ecosystems and volume VIa included sites in sand hill, sand pine scrub, and white pine-invaded hardwood ecosystems in the Southeast. Volume VII included sites in Oregon white oak, California deciduous oak, and mixed-conifer with shrub ecosystems in Washington, Oregon, and California. Volume VIII included sites in hardwood, pitch pine, and red spruce/balsam fir ecosystems in the Northeast. Volume IX included sites in oak/juniper ecosystems in southern Arizona and New Mexico. Volume X included sites in sagebrush with grass and ponderosa pine-juniper ecosystems in central Montana. An unnumbered volume included grassland, shrubland, woodland, and forest ecosystems in Hawaii.

In the printed publications, sites generally include wide-angle and stereo-pair photographs supplemented with information on living and dead fuels, vegetation, and stand structure and composition within the area visible in the photographs (fig. 1).

Figure 1--Photo series sample area layout. Forty random azimuth line transects (one at each point on the 30- and 150-foot arcs, and two at each point on the 60-, 90-, and 120-foot arcs) and 10-15 clipped vegetation plots (two to three per arc) were located within the sample area. Trees, shrubs and seedlings were inventoried on 12 systematically located sample plots.
Figure 1--Photo series sample area layout. Forty random azimuth line transects (one at each point on the 30- and 150-foot arcs, and two at each point on the 60-, 90-, and 120-foot arcs) and 10-15 clipped vegetation plots (one to three per arc) were located within the sample area. Trees, shrubs and seedlings were inventoried on 12 systematically located sample plots.

WHY IS THE PHOTO SERIES NEEDED?
These photo series are land management tools that can be used to assess landscapes through appraisal of living and dead woody material and vegetation (i.e., fuels) and stand characteristics. Once an assessment has been completed, stand treatment options, such as prescribed fire, mechanical or hand fuel reduction, or harvesting, can be planned and implemented with greater detail and precision to better achieve desired effects while minimizing negative impacts on other resources.

The photo series has application in several branches of natural resource science and management. Inventory data such as these can be used as inputs for evaluating animal and insect habitat, nutrient cycling, and microclimate, for example. Fire managers will find these data useful for predicting fuel consumption, smoke production, fire behavior, and fire effects during wildfires and prescribed fires. In addition, the photo series can be used to appraise carbon sequestration, an important factor in predictions of future climate, and to link remotely sensed signatures to live and dead fuels on the ground.  The photos have proved useful in discussions of proposed treatment options with citizens, public officials, and agency administrators. They are also a practical communication tool in the preparation, advertisement, and administration of fuel treatment contracts.

Ground-based inventory procedures that directly measure site conditions (e.g., fuel loading and arrangement, vegetation structure and composition, etc.) exist for most ecosystem types and are useful when a high degree of accuracy is required. Ground-based inventory is time consuming and expensive, however. Photo series can be used to make quick, easy, and inexpensive determinations of fuel quantities and stand conditions when less precise estimates are acceptable.

HOW WAS THE PHOTO SERIES DEVELOPED?
Sites photographed for the series were selected to show a range of conditions of several site attributes depending on the ecosystem type. Photographs were taken, and fuel loading, stand structure, and composition data were collected by using the procedures of Maxwell and Ward (1980) as a guide.

PHOTOGRAPHS
The digital photo series displays one wide-angle photograph per site.  Most printed volumes also include stereo-pair photographs.  The marker in these photographs is a 1-foot square, and the pole is painted in contrasting colors at 1-foot intervals to provide scale. The pole is 30 feet from the camera. The summary data relate to the field of view of the stereo-pair photograph and are based on measurements taken in the sample area only (see fig. 1). No sampling occurs in the foreground between the camera and the sign.

USING THE PHOTO SERIES
The natural fuels photo series is a tool for quickly and inexpensively evaluating a variety of fuel and vegetation conditions. Because of its ease of use, however, care must be taken when evaluating field sites to compare only with photo series sites that are appropriate matches. It is acceptable, however, to use the data from more than one site from the photo series when evaluating a site in the field (e.g., woody material loading from one site in the photo series and tree density from another site in the photo series to best match the conditions of a given field site).

Make a visual inventory of the site by observing fuel and stand conditions within the field of view and comparing them with the stereo-pair photographs as follows, remembering that the data tables relate to the area behind the sign in the stereo-pair photographs:

The total loading or stand condition can then be calculated by summing the estimates. If the site being inventoried has areas with obvious differences in woody material or stand conditions, the user should make separate determinations for each area and then weight and cumulate the loading for the whole site.

Characteristics not distinguishable in the photographs are forest floor depth, loading, and bulk density, and proportions of sound and rotten woody material. If values for these characteristics are desired in the inventory, they must be derived from independent sampling or observations.

The 20 National Fire-Danger Rating System fuel models (Burgan 1988, Deeming et al. 1977) and the 13 original (Albini 1976) or 40 new (Scott and Burgan 2005) fire behavior fuel models are very general in content and broadly applied.  Each photo series encompasses a wider range of conditions, and individual sites represent fuel characteristics at greater resolution than can be gained by using fuel models; consequently, we chose not to assign one of these existing fuel models or types to individual sites in the photo series. The photo series was designed to provide sufficient fuel and vegetation data from which managers could generate their own customized fuel models or types.


METRIC CONVERSIONS
1 inch (in) = 2.54 centimeters
1 foot (ft) = 0.3048 meter
1 square foot = 0.0929 square meter
1 acre (ac) = 4,046.9 square meters
1 acre = 0.4047 hectare
1 pound (lb) = 0.4536 kilogram
1 ton = 0.9072 metric ton
1 ton = 907.2 kilograms
(°F - 32) (5/9) = °C
1 pound/acre (lb/ac) = 1.1209 kilogram/hectare
1 pound/acre = 1.1209 E-04 kilograms/square meter
1 ton/acre = 0.2242 kilogram/square meter
1 ton/acre = 2,241.7023 kilograms/hectare
1 ton·acre-1·inch-1 = 8.8256 kilograms/cubic meter
1 ton·acre-1·inch-1 = 8,825.6 grams/cubic meter
1 ton·acre-1·inch-1 = 8.8256 E-03 grams/cubic centimeter

LITERATURE CITED

Albini, F.A. 1976. Estimating wildfire behavior and effects. Gen. Tech. Rep. INT-30. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 92 p.

Burgan, R.E. 1988. 1988 revisions to the 1978 national fire-danger rating system. Res. Pap. SE-273. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station. 39 p.

Deeming, J.E.; Burgan, R.E.; Cohen, J.D. 1977. The national fire-danger rating system--1978. Gen. Tech. Rep. INT-39. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Forest and Range Experiment Station. 63 p.

Maxwell, W.G.; Ward, F.R. 1980. Guidelines for developing or supplementing natural photo series. Res. Note PNW-358. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 16 p.

Rollins, M.G.; Frame, C.K., tech. eds. 2006. The LANDFIRE prototype project: nationally consistent and locally relevant geospatial data for wildland fire management. Gen. Tech. Rep. RMRS-GTR-175. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 416 p.

Scott, J.H.; Burgan, R.E. 2005. Standard fire behavior fuel models: a comprehensive set for use with Rothermel’s surface fire spread model. Gen. Tech. Rep. RMRS-GTR-153. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 72 p.