Swanson, S., Schultz, B., Nova-Echenique, P., Dyer, K., McCuin, G., Linebaugh, J., Perryman, P., Tueller, P., Jenkins, R., Scherrer, B., Vogel, T., Voth, D., Freese, M., Shane, R., McGowan, K. 2018, Nevada Rangeland Monitoring Handbook (3rd) || Appendix J - Use Mapping, Key Species Method and Proper Use, Extension | University of Nevada, Reno, SP-18-03

Use Mapping

Use pattern mapping is an excellent way to understand how grazing by livestock, wildlife, horses and burros, ground squirrels, etc. connect to the rangeland resource in larger pastures. Across the West, livestock distribution is commonly the greatest management problem and opportunity. Distribution varies according to slope, aspect, location of waters, palatability of forages, patterns of residual forage, season of use, animal habits, etc.

The best kind of base map for delineation of use zones is an aerial photo or orthophotoquad showing soils or ecological sites and physical features, such as fences, waters and roads. Other kinds of maps commonly used include 1:24,000 topographic maps, 1:000,000 maps or even rough sketches (Figures 23 and 66). The mapping procedure involves traversing the pasture to obtain a general concept of how the vegetation has been utilized and the pattern of this utilization. Features such as topography, rockiness, ecological sites, vegetative types and distance from water affect grazing patterns. They are helpful in denoting the extent of use zones and mapping their boundaries.

Commonly used classes of use levels are: 0-5, 6-20, 21-40, 41-60, 61-80, 80-94, and 95-100 percent. Other classes can be used to maintain continuity with an existing management plan or monitoring data set. Use classes and an approach to judging the degree of utilization are discussed under Key Species Method Utilization on page 23 of the Interagency Technical Reference “Utilization Studies and Residual Measurements” (BLM 1999b) and in the Ranchers’ Monitoring Guide (Perryman et al. 2006). Key species utilization on key areas can be used as a component of use pattern mapping. However, use pattern mapping based only on key areas misses most of the pattern.

Mapping proceeds by traversing the pasture. When another use zone is observed, the level of the new use class and approximate boundary of the zone are recorded on the map together with the other information. Other information recorded for each traversed use zone includes name(s) or symbol(s) of the key species and other common species that were routinely grazed, and other allotment- or site-specific observations or indicators that relate to the level and pattern of grazing use. Further traversing extends boundaries of use zones until the entire pasture has been observed, then the approximate number of acres within each use zone is recorded on the map as illustrated in the Ranchers’ Monitoring Guide (Perryman et al. 2006).

The timing for utilization mapping depends on objectives. Commonly, use mapping and utilization measurement occurs at the end of the growing season or the end of the grazing season, whichever occurs later. It is important to observe utilization during the grazing period to observe use zones as they develop. Such data or even observations would be very useful for applying the grazing response index (on page 48 or in the Ranchers’ Monitoring Guide by Perryman et al. (2006)). A seasonal use map provides early indications of grazing issues (e.g. distribution or differential use by different species).

Lumping or averaging species for utilization monitoring may miss key information. The exception is an area with several forage species of approximately equal palatability, production and grazing accessibility at the same time of year. Such circumstances are most likely to occur in wet meadows, riparian areas or seedings. Under these conditions, utilization may be judged for a community rather than for a key species. For example, degree-of-use of mountain meadow sites could be represented by an average use recorded on the part of the plant community that produces the bulk of the forage. Because vegetation is needed for riparian functions, specifically note the vegetation that relates to these functions, such as at the water’s edge, the greenline.

Use Pattern Map of the Hubbard Vineyard allotment in 2008
Figure 66. Distribution of grazing intensity can be influenced by season of use, weather, infrastructure, such as fences and location or number of waters, topography, stockmanship, placement of supplement, past use patterns, and animal selection or training. Mapping use patterns provides clues for management and selection of monitoring locations, as well as a record of use in a given year to interpret long-term monitoring.

Use patterns often remain similar from year to year for a variety of reasons. However, utilization patterns can change because of management actions including development of water, herding, season of use, culling, changing kind or class of livestock, etc. The number of years of data needed for interpretation varies depending on the variation from year to year. Once use patterns are understood, they may suggest management changes that should be considered to adjust the use pattern. These changes should be tied to objectives and opportunities for enhancing rangeland, plant or animal health. Management changes that affect distribution include use of stockmanship to place livestock, other herding, water locations, season of use, use or placement of supplements or salt, changing pasture size or shape, animal numbers, duration of grazing period, fire, vegetation type conversions, etc.

Key Species Method

The key species method (formerly the modified key forage plant method) is based on an ocular estimate of the amount of forage removed by weight on key species. This method is described in the interagency technical reference on utilization studies and residual measurements (BLM 1999b) and in the Ranchers’ Monitoring Guide (Perryman et al. 2006).

Training for this utilization method requires observers to compare their ocular observations of use with the clipped and weighed amount using ungrazed plants. Observations are recorded in one of seven utilization classes, as is common in use mapping. Utilization cages can be employed in conjunction with this method on key areas to provide reference plants to observe while reading a study or to clip while training. Utilization cages must be relocated annually to protect randomly chosen but representative plant(s) of the key species in similar growing conditions. The utilization determined on key areas is used in combination with actual use data, trend in species composition, use patterns, weather, and/or supplementary information to evaluate whether or not management changes are needed.

While key species utilization is broadly applicable, compare this method with other utilization/residual forage methods to choose the one that best addresses site-specific conditions and objectives. For example, residual vegetation is preferred in areas where vegetation is relatively evenly dispersed, such as meadows or where growing the next crop of annual brome grasses prevents transition to an even more degraded state. For guidance related to monitoring the use of woody plants, also see the Interagency Technical Reference “Utilization Studies and Residual Measurements” (BLM 1999b).

Proper Use

Proper use is a degree of utilization of current year’s growth that, if continued, will achieve objectives (Bedell 1998). Proper use is species specific. It may also be affected by the ecological site, state and phase, and varies to a great degree with neighboring plants, the opportunity for plants to grow or regrow, season of use, and duration and intensity of use.

Determination of key species and desired proper use is part of the planning process. Local specifications for acceptable degree of use should be based upon research data and on the experience of the manager and range user to achieve objectives. Considerations of proper use often drive targets for within season triggers and end-of-season indicators in allotment management or multiple-use management plans. Proper use, based on grazing management and setting, should be checked against trend data to determine if the current proper use is appropriate or needs adjustment.

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Also of Interest:

Economic Analysis of Management Options Following a Closure of BLM Rangeland Options due to Sage Grouse Population in Elko County. Richardson, J., B. Herbst, and T. Harris. 2014, University Center for Economic Development, University of Nevada, Reno, University Center for Economic Development Technical Report, UCED 2013-14-15.
Conservation Plantings for Natural Resources Management: Rangelands, Windbreaks, Wildlife Habitat, Soil Protection, Conservation Cover, and Mined Land Reclamation. Joint recommendations Tueller, P. T., G. K. Brackley, J. Briggs, J. W. Doughty, G. Staidl, and S. Swanson. 1992, Univ. of NV Coop. Ext. and the U. S. Soil Cons. Serv. BE-92-01 Repl.C-183.
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