This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Restoration of Native Shrubland in a Military Training Area Using Hand-Broadcasting of Seed Dana L. Quinney Marj McHenry Jay Weaver The authors decided to try hand-broadcast seeding as a low-impact method of creating "source islands" of big sagebrush in large wildfire burns dominated by Poa secunda, Poa secunda and exotic annuals, or exotic annuals only. The seeding sites were areas where few or no native shrubs had been present for fifteen years or more (Quinney and others, unpublished report, maps, and data, Boise District BLM; personal observation), indicating that natural restoration was very slow or absent. Hand-broadcasting made it possible to seed into the most promising microsites present (drainage draws, snowdrifts, and the like), taking advantage of pockets of soil moisture, with little soil disturbance. Ahstract-The Idaho Army National Guard trains on the Orchard Training Area, 55,848 hectares ofBLM shrub-steppe in southwestern Idaho. Historically, grazing, wildfire, and military training have converted thousands of hectares of big sagebrush into stands of exotic annuals. Other areas remain in good condition. Handbroadcasting of sagebrush seed can introduce "source islands" of shrubs into areas where sagebrush has been removed by fire. In the Orchard Training Area, fires caused by lightning, railroad traffic, military training, and arson, have burned thousands ofhectares of native shrub-steppe during the past fifteen years; most significant burns occurred in the early 1980s (Boise District, U.S.D.l. Bureau of Land Management unpublished fire data). To determine which species to plant at which sites, various sources are used, including A Grazing History of Southwestern Idaho (Yensen 1980) and a set of vegetation maps with an accompanying report and plant transect summaries, produced by Boise District Bureau of Land Management biologists in 1981. In this effort, vegetation polygons in the Snake River Birds of Prey Area greater than 16 hectares were mapped, ground-truthed, and sampled (Quinney and others, Boise District BLM, unpublished report, maps, and data). When possible, ecotypic seed is collected in the training area; otherwise, commercial seed is used. Since 1988, several thousand hectares have been planted to native shrub, grass, and wildflower species. Vegetation restoration in the southwestern Idaho desert poses a challenge. Because of the fine, friable soils; low, irregular precipitation; multiple land uses; and exotic weeds; traditional seeding methods may fail. Every land manager who has seeded into desert environments has encountered the problem of "good year for seed, bad year for planting." With sagebrush and some other Great Basin natives, seed must be planted before viability is lost, regardless of the precipitation. Also, in the authors' experience, mechanical disturbance of the soil surface by some seeding equipment may result in invasion of exotic annuals, and/or destruction ofthe cryptogamic soil crust and consequent wind erosion. Methods _ _ _ _ _ _ _ _ __ Twelve sites in Ada County, Idaho, were hand-broadcast with commercially obtained Wyoming big sagebrush seed during the winter of 1992-1993. These sites were small (six or fewer hectares). The sites were not exclosed from military training and are grazed in spring and fall by sheep and/or cattle. All sites supported Wyoming big sagebrush communities in 1979, according to the BLM maps and transect summaries identified above (Quinney and others, Boise District BLM unpublished report, maps, and data). Seeding of each site was accomplished in from one to three hours by one or two people. Seeding rates at each site are shown in figure 1. Rates are approximations derived from driving or walking the perimeter of the seeded sites with a global positioning system to determine the area, and dividing the number of pounds of seed (PLS) used at the site by the number of hectares; seed distribution within a site was not uniform. I I I SITE CURLEW I VALLEY LITHO I OBSIDIAN I PIT ! LBS/HECTARE In: Barrow, Jerry R.; McArthur, E. Durant; Sosebee, Ronald E.; Tausch, Robin J., comps. 1996. Proceedings: shrubland ecosystem dynamics in a changing environment; 1995 May 23-25; Las Cruces, NM. Gen. Tech. Rep. INT-GTR-338. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. Dana L. Quinney, Marj McHenry, and Jay Weaver are Biologists for the State of Idaho Military Division Office of Environmental Management, 4715 S. Byrd Street, Boise, ID 83705. 1.98 2.69 3.29 Figure 1-Seeding rates and densities of Artemisia tridentatafor five sites in the Orchard Training Area, Idaho. 156 2.96 1.65 52 Hand broadcasting of seed creates irregular, ribbonlike bands of seedlings. These irregular bands are difficult to sample with straight-line transects. A modified Daubenmire (1979) method of canopy coverage sampling was used. An arc-azimuth method was used to layout sampling transects on bands of seedlings, allowing for random placement of the measuring frame within a degree arc the width of the band at the distance where the next measurement was to be made. After the point of origin of each transect, a measuring frame was dropped and read at five-meter intervals. The location of the next measuring frame was five meters from the previous one, centered about a point perceived by using a sighting compass at the previous frame-center point and determining the arc of seedlings. Then, from a randomnumber table, the first number that fell within this degreearc was chosen as the center point for the next frame. Frame center points were marked with 45-cm steel rods. At each site, four 20-frame transects were established, two in seedling bands and two control transects in unseeded interspaces. Five of the twelve sites, Curlew, Valley, Lithophragma, Obsidian, and Pit, were monitored in 1995. Within each frame, the following percents canopy cover were estimated: cover for each vascular plant species, cryptogamic cover, grass litter, forb litter, shrub litter, cow/sheep litter. Stem ground cover was also estimated. Within each frame, big sagebrush individuals were counted and their heights recorded to the nearest half-centimeter. Two photographs were taken from a fixed height and location at the first frame of each transect, a frame vertical and a panorama. Annual monitoring of the sites is planned. Four sites had an understory ofPoa secunda. One site, Pit Road, had little grass, but an abundance of annual weeds, includingRanunculus testiculatus and Lepidium perfoliatum. Hand-broadcasting of sagebrush seed was successful on all sites, regardless of the presence, absence, or dominance of the site by native perennial Poa (fig. 2). Results 48 44 40 36 32 28 24 CURLEW II VALLEY SAGE SEEDLINGS LITHO OBSIDIAN • PIT PERENNIAL. GRASSES Figure 2-Artemisia tridentata seedling density and canopy cover of native perennial grasses for five sites in the Orchard Training Area, Idaho. Since sagebrush transects were placed only within bands of seedlings, of course, only areas where seedlings appeared were sampled. Control transects characterize the sites' vegetation where no seedlings occurred. Preliminary results indicate only that big sagebrush seedlings did appear in the areas seeded. Subsequent annual monitoring will evaluate the success ofthis method of shrub restoration through time. References ------------------------------- Daubenmire, R. A canopy-coverage method of vegetational analysis. Northwest Science 33(1): 43-64. Quinney, D. L., Smith, G. W., Nydegger, N. Vegetation Patterns of the Snake River Birds of Prey Area, unpublished report, maps, and data, U.S. Department of the Interior, Boise District Bureau of Land Management. Yensen, D. L. 1980. A grazing history of southwestern Idaho, with emphasis on the Snake River Birds of Prey Area. U.S. Department of the Interior, Boise District Bureau of Land Management. 82 p. U.S. Department of the Interior, Boise District Bureau of Land Management. Unpublished fire maps and data. ----------------------------------- Preliminary results indicate that hand-broadcasting of big sagebrush can be a viable restoration procedure in the southwestern Idaho desert. Sagebrush broadcast see dings can produce seedlings in areas dominated by weeds, and also in areas dominated by Sandberg's bluegrass (fig. 2). Handbroadcasting of sagebrush into small sites is economical, does not disturb the soil, and can succeed in dry years because the most favorable micro sites can be seeded. 157