Lincoln County is located in eastern Nevada, adjacent to the Utah/Nevada border and immediately north of Clark County, Nevada. Lincoln County is approximately 6.8 million acres in size. A jurisdictional summary of land management administration and coverage including water is provided in Table 3-1 and presented in Figure 3-1. The majority of land within Lincoln County is administered and managed by the Bureau of Land Management. The federal land management policies and decisions on the wildland-urban interface land will have direct effects on private landowners within Lincoln County.
Land Administrator | Approximate Acreage | Percent of County |
---|---|---|
Bureau of Land Management | 5,604,415 | 82 |
Forest Service | 29,347 | <1 |
Department of Defense | 772,736 | 12 |
Fish and Wildlife Service | 268,723 | 4 |
State of Nevada | 5,733 | <1 |
Private | 122,815 | 2 |
Water | 2,622 | <1 |
Approximate values derived from the BLM landownership GIS database. The land administrator for surface waters in Lincoln County was not available in the database. |
The Nevada State Demographer estimated the 2003 population for Lincoln County at 3,749 persons. The Nevada Department of Employment, Training, and Rehabilitation listed trade, government, and service industries as the major employer types in the County. (Nevada Commission on Economic Development, 2004).
Elevations within the county range from 10,310 feet in the Schell Creek Range in the northern portion of the county, to approximately 1,760 feet at Town Wash in the southeast corner of the county. Primary mountain ranges include the southern extent of the Schell Creek Range, the Delamar Mountains, the Meadow Valley Mountains, and the Pahranagat Range. Part of the Desert National Wildlife Range extends into the southwestern portion of the county, as does a small portion of the Nellis Air Force Range.
Several large wildfires have occurred in the recent history of Lincoln County. Between 1980 and 2003, 423,876 acres (approximately six percent of Lincoln County) burned in wildland fires. According to information in the BLM database, the largest fire recorded in the county was a 21,805-acre fire in 1999 at the south end of the Delamar Mountains. Table 3-2 summarizes the fire histories and fire ignitions recorded by year for public lands within Lincoln County. Figure 3-2 illustrates the recorded fire history in the vicinity of Lincoln County. Several wildland fires may have occurred on private lands within the county, however, these fires are not always reported to federal agencies and are therefore not reflected in Table 3-2 or Figure 3-2.
Year | Number of Fire Ignitions | Total Fire Acreage |
---|---|---|
1980 | 110 | 32,860 |
1981 | 80 | 158 |
1982 | 46 | 196 |
1983 | 47 | 444 |
1984 | 65 | 16,714 |
1985 | 94 | 8,185 |
1986 | 149 | 27,046 |
1987 | 112 | 2,060 |
1988 | 83 | 13,667 |
1989 | 65 | 9,215 |
1990 | 81 | 584 |
1991 | 83 | 51 |
1992 | 65 | 2,447 |
1993 | 78 | 37,238 |
1994 | 177 | 54,980 |
1995 | 57 | 676 |
1996 | 278 | 69,334 |
1997 | 71 | 9,776 |
1998 | 99 | 15,404 |
1999 | 160 | 40,227 |
2000 | 195 | 61,244 |
2001 | 125 | 1,962 |
2002 | 131 | 18,693 |
2003 | 103 | 715 |
TOTAL | 2,554 | 423,876 |
Source: Fire history data provided by the National Interagency Fire Center, Boise, Idaho. Fire acreage is derived from BLM and USFS fire perimeter data and specific to fire acreage within Lincoln County. |
Ignition risks for wildfires fall into two categories: lightning and human caused. Human caused ignitions can come from a variety of sources: fires started along roads from burning material thrown out of vehicle windows or ignited during auto accidents; off-road vehicles; railroads; arcing power lines; agricultural fires; ditch burning; debris burning in piles or burn barrels; target shooting; unattended campfires; and fireworks. The ignition source records for Lincoln County indicate that for 2,554 fire incidents, 2,034 were due to lightning, 479 were human caused, and 41 were of unknown origin.
The science of fire ecology is the study of how fire contributes to plant community structure and species composition. A “fire regime” is defined in terms of the average number of years between fires under natural conditions (fire frequency) and the extent to which dominant vegetation is replaced by fire (fire severity). Natural fire regimes have been affected throughout most of Nevada by twentieth century fire suppression policies. Large areas that formerly burned with high frequency but low intensity (fires more amenable to control, suppression, and rehabilitation) are now characterized by large accumulations of unburned fuels, which once ignited, will burn at higher intensities.
Big sagebrush communities are the most common vegetation types in Nevada with an altered fire regime, now characterized by infrequent, high-intensity, catastrophic fires. Sagebrush requires ten to twenty years or more to reestablish on burned areas, and most often these areas provide the conditions for establishment and spread of invasive species before sagebrush reestablishment can occur. Cheatgrass is the most common invasive species to reoccupy sagebrush and pinyon-juniper burned areas in northern Nevada.
Cheatgrass is a common, introduced annual grass that aggressively invades disturbed areas, especially burns. Replacement of a native shrub community with a pure stand of cheatgrass increases the susceptibility of an area to repeated wildfire ignitions, especially in late summer when desiccating winds and lightning activity are more prevalent. The annual production, or volume of cheatgrass fuel produced each year, is highly variable and dependent on winter and spring precipitation. Plants can range from only a few inches tall in a dry year to over two feet tall on the very same site in wet years. In a normal or above normal precipitation year, cheatgrass can be considered a high hazard fuel type. In dry years, cheatgrass is generally sparse and low in stature and poses a low fire behavior hazard because it tends to burn with a relatively low intensity. However, in both wet and dry years, dried cheatgrass creates a highly flammable fuel bed that is easily ignited with the propensity to rapidly burn into adjacent cover types that may be characterized by more severe and hazardous fire behavior. The ecologic risk of a fire spreading from a cheatgrass stand into adjacent, unburned native vegetation is that additional disturbed areas are thereby opened and vulnerable to cheatgrass invasion. Associated losses of natural resource values such as wildlife habitat, soil stability, and watershed functions are additional consequences.
Eliminating cheatgrass is an arduous task. Mowing defensible space and fuelbreak areas annually before seed maturity is effective in reducing cheatgrass growth. In areas where livestock may be utilized, implementing early-season intensive grazing up to and during flowering may aid in depleting the cheatgrass seed bank and reduce the annual fuel load (BLM 2003, Davison and Smith 2000, Montana State University 2004). It may take years and intensive treatment efforts to control cheatgrass in a given area, but it is a desirable conservation objective in order to revert the landscape to the natural fire cycle and reduce the occurrence of large, catastrophic wildfires. Community-wide efforts in cooperation with county, state, and federal agencies are necessary for successful cheatgrass reduction treatments.
Singleleaf pinyon and Utah juniper are the dominant components of a plant community commonly referred to as Pinyon-Juniper (P-J). P-J woodlands were primarily confined to the steeper slopes normally found at higher elevations in the Great Basin prior to European settlement. These woodland communities were characterized by a discontinuous distribution on the landscape and a heterogeneous internal fuel structure: a mosaic pattern of shrubs and trees resulting from the canopy openings created by small and frequent wildfires.
Both pinyon and juniper trees have relatively thin bark with continuous branching all the way to the ground. In dense stands, lower tree branches frequently intercept adjacent ladder fuels, e.g. shrubs, herbaceous groundcover, and smaller trees. This situation creates a dangerous fuel condition where ground fires can be carried into tree canopies, often resulting in crown fires. A crown fire is the most perilous of all wildfire conditions and is usually catastrophic in nature since the danger to firefighters is generally too great to deploy ground crews.
Critical features at risk of loss during a wildfire event can be economic assets such as agricultural and industrial resources or cultural features, such as historic structures, archaeological sites, and recreation-based resources.
There are five sites listed on the National Register of Historical Places for Lincoln County. The Nevada State Register of Historical Places lists one site. The effects of fire on cultural and historical resources depend upon factors that vary from place to place such as fuels, terrain, and type of cultural or historical buildings and resources present. Archeological sites and historic trails are not necessarily vulnerable to wildfire impacts. Historic districts, historic buildings, and resources in the wildland-urban interface communities in Lincoln County that could be negatively impacted by wildfire are summarized in Table 3-3.
Site Name | Location | Source Register |
---|---|---|
1938 Lincoln County Courthouse | Pioche | National Register of Historic Places |
Bristol Wells Town Site aka Bristol City | Pioche | National Register of Historic Places |
Brown’s Hall - Thompson’s Opera House | Pioche | National Register of Historic Places |
Caliente Railroad Depot aka Caliente Station |
Caliente | National Register of Historic Places |
Lincoln County Courthouse | Pioche | National Register of Historic Places |
Smith (Scott) Hotel | Caliente | Nevada State Register of Historic Places |
Potential habitat is present in Lincoln County for six species listed as threatened or endangered under the Endangered Species Act. An additional twenty species are protected by state legislation (Nevada Natural Heritage Program database; last updated for Lincoln County March 18, 2004). These species are identified in Table 3-4. The Nevada Natural Heritage Program, the Nevada Division of Forestry, and the Nevada Department of Wildlife should be consulted regarding specific concerns and potential mitigation to minimize impacts to these species prior to implementing fuel reduction projects and prior to the occurrence of a catastrophic wildfire.
Scientific Name | Common Name | Legislation |
---|---|---|
Plants | ||
Astragalus geyeri var. triquetrus | Threecorner milkvetch | NRS 527.260.300 |
Astragalus mohavensis var. hemigyrus | Halfring milkvetch | NRS 527.260.300 |
Eriogonum viscidulum | Sticky buckwheat | NRS 527.260.300 |
Optunia pulchella | Sand cholla | NRS 527.060.120 |
Sclerocactus schlesseri | Schlesser pincushion | NRS 527.060.120 |
Spiranthes diluvialis | Ute lady’s tresses | NRS 527.260.300 |
Fish | ||
Catostomus clarki ssp. (unnamed) | Meadow Valley Wash desert sucker | NRS 501 |
Crenichthys baileyi baileyi | White River springfish | ESA-Listed Endangered NRS 501 |
Crenichthys baileyi grandis | Hiko White River springfish | ESA-Listed Endangered NRS 501 |
Gila robusta jordani | Pahranagat roundtail chub | ESA-Listed Endangered NRS 501 |
Lepidomeda mollispinis mollispinis | Virgin River spinedance | NRS 501 |
Lepidomeda mollispinis pratensis | Big Spring spinedace | ESA - Listed Threatened NRS 501 |
Rhinichthys osculus ssp. unnamed | Meadow Valley speckled dace | NRS 501 |
Rhinichthys osculus velifer | Pahranagat speckled dace | NRS 501 |
Rhinichthys sp. (unnamed) | Pahranagat dace | NRS 501 |
Reptiles | ||
Gopherus agassizii | Desert tortoise (Mojave Desert population) |
ESA - Listed Threatened NRS 501 |
Heloderma suspectum cinctum | Banded gila monster | NRS 501 |
Mammals | ||
Euderma maculatum | Spotted bat | NRS 501 |
Birds | ||
Athene cunicularia hypugaea | Western burrowing owl | NRS 501 |
Buteo regalis | Ferruginous hawk | NRS 501 |
Buteo swainsoni | Swainson’s hawk | NRS 501 |
Coccyzus americanus occidentalis | Western yellow-billed Cuckoo | NRS 501 |
Empidonax traillii extimus | Southwestern willow flycatcher | ESA - Listed Endangered NRS 501 |
Ixobrychus exilis hesperis | Western least bittern | NRS 501 |
Otus flammeolus | Flammulated owl | NRS 501 |
Phainopepla nitens | Phainopepla | NRS 501 |
Approximately 269,000 acres of the Desert National Wildlife Refuge extend into southwest Lincoln County. The US Fish and Wildlife Service administers the Refuge, which was established primarily for perpetuating the desert bighorn sheep and its habitat. Camping, hiking, backpacking, horseback riding, bird watching and limited hunting are all popular activities enjoyed by refuge visitors. Wildfires in the area would damage wildlife habitat and could cause a reduction in visitor days in the Refuge, potentially causing economic losses in the surrounding communities.
In August 2002 a team of specialists from Resource Concepts, Inc. conducted Wildfire Risk/Hazard Assessments in four Lincoln County Communities: Caliente, Mt. Wilson, Panaca, and Pioche/Caselton Heights. Each community is included in a separate community chapter in this report, with a summary of the 2002 RCI risk assessment, fuel reduction plans, and descriptions of completed treatments.
Acoma | 300 acres | Tree thinning |
Clover Mountain Ponderosa Restoration | 800 acres | Pinyon-Juniper removal and prescribed burn |
Ella Mountain | 38 acres | Brush removal and tree thinning |
Sage Grouse Lek Improvement | 26,000 acres | Tree and brush thinning |
Sheep Flat Restoration | 4,300 acres | Prescribed fire |
For additional information on the proposed fuel reduction treatments in Lincoln County, contact either the BLM Ely Field Office or Caliente Field Station Fire Management Specialist/Fuels Program Manager.
Figure 3-1Community Locations and Land Ownership, Lincoln County, Nevada |
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Figure 3-2Fire History and Critical Features Potentially At Risk, Lincoln County, Nevada |