Ecological Assessment of Potential Wilderness Areas in the Klamath~Siskiyou Region of North Western California
Chris Trudel, Curtice Jacoby, Karin Riley-Thron, Per Tillisch
LEGACY – The Landscape Connection, 830 G Street Suite 220, Arcata, CA 95521, www.legacy-tlc.org, (707) 826-9408
Project made possible by:

Funding from: World Wildlife Fund - Klamath Siskiyou Program, Dr. Dominick DellaSala, Ashland, Oregon.
Hardware and software support from: Conservation Technology Support Program, Environmental Systems Research Institute, Redlands, California.
Introduction
U.S. Senator Barbara Boxer and U.S. Representative Mike Thompson are considering forty-six potential wilderness areas (PWAs) in the Klamath-Siskiyou region of northwestern California for wilderness designation. The northern California portion of the Klamath-Siskiyou Ecoregion contains many unprotected roadless areas of varying sizes and ecological importance. Recently, Strittholt and DellaSala (2001) published a paper in Conservation Biology generally documenting the importance of roadless areas in the Klamath-Siskiyou Ecoregion and providing ecological attribute information on roadless areas greater than 1,000 acres. The California Wild Heritage Campaign (CWHC) is now proposing legislation to protect millions of acres of land that are mapped as PWAs across the state and in the northern California portion of the Klamath-Siskiyou ecoregion. However, the PWAs mapped by CWHC have no documented ecological attribute information from which to support their inclusion in the proposed wilderness legislation.
The purpose of this report is to document the individual contribution of the PWAs to a regional reserve design for the California portion of the Klamath-Siskiyou region. The information contained in this report documents the important ecological contribution the PWAs make to the regional reserve system of the Klamath~Siskiyou Ecoregion in northwestern California. The information will be used to assist the CWHC, conservation groups, and legislators in documenting the importance of PWAs in the Klamath-Siskiyou ecoregion and ensuring their inclusion in the proposed wilderness legislation.
In order to qualify as a PWA, the area must be roadless and on public lands. Roadless areas are important in maintaining biodiversity in the Klamath~Siskiyou Ecoregion (Strittholt and DellaSala 2001). The review of the ecological effects of roads by Trombulak and Frissell (2000) documents the immense ecological impacts of roads on natural systems. The impacts of roads vary from direct habitat loss due to removal of vegetation during road construction, to an increase in animal mortality from automobile collisions, increased access to hunters, trappers, and poachers, to a long-term disruption of the physical environment through fragmentation of both the terrestrial and aquatic ecosystems and introduction of invasive exotic species. Moreover, roads can elevate fire risks due to the association between greater vehicle access and increased risk of fire from accidental or arson related fires (DellaSala et al. 1995). The Klamath-Siskiyou ecoregion has nearly 40,000 miles of forest roads, enough to make more than 65 roundtrips between Medford to Portland (Strittholt and DellaSala 2001). Given the negative effects of roads on ecological systems and the importance of roadless areas to the conservation of biodiversity, it is imperative that these last remaining roadless areas be given adequate protection.
Methods:
The ecological attribute information used in the Strittholt and DellaSala (2001) study of roadless areas was transferred to the northern California portion of the Klamath-Siskiyou ecoregion PWAs provided by the CWHC. Presence of salmonid species was included as a special element and the Holland community vegetation types from the California Gap Analysis Project (GAP) were used as a substitute to the physical habitat types used by Strittholt and DellaSala (2001) for ecosystem representation.
The analysis was performed using both ArcInfo 8.1.2 and ArcView 3.2 GIS software. The PWAs that intersected with the Klamath-Siskiyou ecoregion boundary were selected from the northern California PWAs coverage and an overlay analysis was performed using each variable. For each PWA and unit the attributes were summarized and recorded in an Excel spread sheet.
Data Sources and Limitations
The spatial data used in this assessment was acquired from a variety of government sources, including the U.S. Forest Service (USFS) and California Department of Fish and Game (CDFG). Themes and sources used can be seen in Appendix A. This data represents the best available information for the time period of this analysis, given the timeline and budget constraints. Due to a delay in a data request from the Siskiyou National Forest (SNF), PWAs for the SNF were analyzed without the inclusion of serpentine, Port-Orford-Cedar (POC), and Salmonid presence. Also, an updated Salmonid presence layer exists (other than which was used) for Six Rivers National Forest (SRF), but needs some processing before it can be incorporated into this assessment.
This report catalogues attributes based on each of the following 6 special elements, 2 representation variables, and 2 ecosystem processes modeled from Strittholt and DellaSala (2001).
Special Element
Representation of Community Types
Ecosystem Process
Elevation – range in feet for each PWA and Unit
Obtaining complete and accurate spatial information for large geographic areas is difficult and some limitations in the data exist. For example, the California Natural Diversity Database (CNDDB) contains locations of element occurrences (EOs) or point locations of species, which have special conservation value (i.e. rare, threatened, endangered, or of special concern). Most surveys only occur in areas with planned management activities and near roads, however, because the PWAs are mostly roadless these areas have not had much survey effort. A PWA without EOs may indicate a lack in survey effort and not that no EOs exist in the PWA.
Late-seral forest data were derived from satellite imagery and were defined as a 30x30-meter area covered by trees with an average size greater than 24 inches diameter at breast height (dbh). Due to the difficulty in using satellite imagery to map tree size, the data may underestimate the amount of actual late-seral forest on the ground.
The Holland classification of terrestrial natural communities provided a basis for agencies to protect and manage rare vegetation throughout California. See Appendix B for a list of Holland types found in the Klamath-Siskiyou with their corresponding rarity ratings and percent representation classes. The fundamental units of Holland’s classification, "natural communities", are defined in terms of habitat, geography, elevation, physiognomy and/or vegetation. The primary shortcomings of the Holland classification are: 1) the lack of uniform criteria in distinguishing the "community" as a fundamental unit, 2) overlapping community descriptions, and 3) uneven resolution with regard to the scale of vegetation that defines each community (Keeler-Wolf 1993, cited in Sawyer and Keeler-Wolf 1995). Regardless of its shortcomings, Holland’s system provides a useful model for identifying and interpreting patterns of diversity across the landscape.
RESULTS
Based on our mapping and analysis of 46 PWAs (Table 1), we describe the attributes for each PWA as a basis for documenting their top ecological attributes for inclusion in wilderness legislation (Appendix C). While all remaining roadless areas warrant protection, this report provides detailed information on the top ecological attributes of importance thereby laying the scientific groundwork for their inclusion in wilderness protections.
Table 1. Potential Wilderness Areas and acreage’s within the Klamath Siskiyou ecoregion organized by their current categorical status in the proposed wilderness legislation. Official CWHC names for PWAs may be different from what is shown here.
|
PWA Name and CWHC Status |
Acres |
|
Primary Areas |
|
|
Trinity Alps |
170,055 |
|
Marble Mountain |
135,562 |
|
Siskiyou |
135,162 |
|
Red Buttes |
61,417 |
|
Snow Mountain |
48,942 |
|
Yolla Bolly Middle Eel |
46,376 |
|
Yuki |
38,608 |
|
Russian |
33,041 |
|
Pattison |
31,011 |
|
Underwood |
16,127 |
|
Sanhedrin Mountain |
10,943 |
|
Mt. Lassic |
10,487 |
|
Mad River Buttes |
6,511 |
|
Secondary Areas |
|
|
Girard Ridge |
42,218 |
|
Chinquapin |
26,130 |
|
South Fork Trinity |
22,671 |
|
Mount Eddy |
18,224 |
|
Chanchellula |
7,825 |
|
Castle Crags |
7,433 |
|
Areas With No Focus |
|
|
Backbone |
23,690 |
|
Devil's Rock |
23,630 |
|
North Fork Eel |
20,478 |
|
Beegum |
19,331 |
|
Panther |
13,405 |
|
Bonanza King |
13,302 |
|
Eagle |
8,522 |
|
Mount Shasta |
6,152 |
|
Unknown Status |
|
|
Grindstone |
51,585 |
|
North Fork Smith |
38,189 |
|
Black Butte |
24,753 |
|
Thomes Creek |
20,117 |
|
Tom Martin |
16,611 |
|
Deer Mountain |
14,998 |
|
Condrey Mountain |
14,840 |
|
Horse Mountain |
12,737 |
|
China Mountain |
11,358 |
|
Soda Mountain |
10,709 |
|
East Fork Mountain |
10,075 |
|
Ship Mountain |
9,642 |
|
Shelly Creek |
8,675 |
|
Cant Hook Mountain |
6,034 |
|
Kelly Peak |
5,636 |
|
Rowdy Creek |
5,364 |
|
Fox Ridge |
5,311 |
|
Donomore Peak |
1,284 |
|
Kalmiopsis |
1,107 |
* Areas with unknown status are unknown due to conflicts between PWA names in the
current PWA GIS coverage and those currently being used by the CWHC.
Backbone Potential Wilderness Area
Shasta-Trinity National Forest
Size = 23,690 acres
Minimum Elevation = 1,066 ft
Maximum Elevation = 4,990 ft
Elevation Range = 3,924 ft
Mean Elevation = 2,304 ft
Backbone PWA has the eighth lowest mean elevation of the PWAs. There are 6,128 acres of late seral forest or 26% of the total area and 84 acres of Permanently flooded Lacustrine Habitat. Within Backbone PWA, the Natural Diversity Database has identified 4 state or global rank rare species occurrences consisting of 2 animal species, 1 plant species, and 1 aquatic species. Backbone PWA contains 1 threatened rare and 1 rare Holland community types. It also contains 7 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Beegum Potential Wilderness Area
Shasta-Trinity National Forest and Bureau of Land Management
Size = 19,331 acres
Minimum Elevation = 1,345 ft
Maximum Elevation = 4,875 ft
Elevation Range = 3,530 ft
Mean Elevation = 3,167 ft
Beegum PWA supplies connectivity between Chanchelluia Wilderness and Yolla Bolly Wilderness. There are 3,935 acres of late seral forest or 20% of the total area. Salmon use a total of 15 miles of the streams, the tenth greatest amount of occupied salmonid habitat of the PWAs. There are 6,361 acres of serpentine or 33% of the area. Beegum PWA has the ninth largest amount of serpentine geology of the PWAs. Within Beegum PWA Natural Diversity Database has identified 3 state or global rank rare species occurrences consisting of 2 plant species and 1 aquatic species. Beegum PWA contains 1 threatened rare and 1 non-ranked Holland community types. It also contains 10 types with less than 25% and one with less than 50% of its distribution represented in a protected area in California. They are listed below.
Black Butte Potential Wilderness Area
Mendocino National Forest
Size = 24,753 acres
Minimum Elevation = 1,640 ft
Maximum Elevation = 5,696 ft
Elevation Range = 4,055 ft
Mean Elevation = 3,645 ft
There are 5,473 acres of late seral forest or 22 % of the total area. Salmonid species use a total of 13 miles of the streams. In Black Butte PW there are 600 acres of serpentine or 2 %. 24,665 acres of Black Butte PWA are located in a designated Northwest Forest Plan Key Watershed or 100 % of the total area. This PWA contains the eighth largest amount of Key Watershed acreage of the PWAs. Within Black Butte PWA the Natural Diversity Database has identified 5 state or global rank rare species occurrences consisting of 4 animal species and 1 aquatic species. Black Butte contains 1 very threatened endangered, 1 threatened rare, and 1 rare Holland community types. It also contains 8 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Bonanza King Potential Wilderness Area
Shasta-Trinity National Forest
Size = 13,302 acres
Minimum Elevation = 2,779 ft
Maximum Elevation = 7,009 ft
Elevation Range = 4,229 ft
Mean Elevation = 4,894 ft
There are 2,712 acres of late seral forest or 20 % of the total area. In Bonanza King PW there is 3,857 acres of serpentine or 29 %. Bonanza King PWA contains 1 very threatened endangered Holland community types. It also contains 4 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Can’t Hook Mountain Potential Wilderness Area
Six Rivers National Forest
Size = 6,034 acres
Minimum Elevation = 115 ft
Maximum Elevation = 2,723 ft
Elevation Range = 2,608 ft
Mean Elevation = 1,255 ft
Can’t Hook Mountain PWA has the lowest mean elevation of the PWAs. Can’t Hook Mountain PWA has 1,392 acres of late seral forest or 23 % of the total area. There is 2,849 acres of Port Orford cedar with 682 acres being infected with the root rot disease. Can’t Hook Mountain PWA has the fifth largest acreage of non-diseased Port Orford Cedars of the PWAs Salmonid species use a total of 8 miles of the streams. In Can’t Hook Mountain PW there are 2,702 acres of serpentine or 45 %. 6,034 acres of Can’t Hook Mountain PWA are located in a designated Northwest Forest Plan Key Watershed or 100 % of the total area. Within Can’t Hook Mountain PWA, Natural Diversity Database has identified 4 state or global rank rare species occurrences consisting of 2 plant species and 2 aquatic species. Can’t Hook Mountain PWA contains 1 very endangered and 1 threatened rare Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Castle Crags Potential Wilderness Area
Shasta-Trinity National Forest
Size = 7,433 acres
Minimum Elevation = 4,800 ft
Maximum Elevation = 7,067 ft
Elevation Range = 2,267 ft
Mean Elevation = 5,866 ft
Castle Crags PWA has 1,111 acres of late seral forest or 15 % of the total area. In Castle Crags PW there are 30 acres of serpentine. Within Castle Crags PWA the Natural Diversity Database has identified 7 state or global rank rare species occurrences consisting of 1 animal species, 5 plant species, and 1 aquatic species. Castle Crags PWA contains 1 threatened endangered, 1 threatened rare, 1 rare and 1 non-ranked Holland community types. It also contains 1 types with less than 25% and 3 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Chanchellula Potential Wilderness Area
Shasta-Trinity National Forest
Size = 7,825 acres
Minimum Elevation = 2,664 ft
Maximum Elevation = 6,168 ft
Elevation Range = 3,504 ft
Mean Elevation = 3,719 ft
Chanchellula PWA has 3,356 acres of late seral forest or 43 % of the total area. Salmonid species use a total of 9 miles of the streams. Chanchellula PWA contains 1 threatened rare and 1 rare Holland community types. It also contains 7 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
China Mountain Potential Wilderness Area
Klamath and Shasta-Trinity National Forests
Size = 11,358 acres
Minimum Elevation = 4,170 ft
Maximum Elevation = 8,520 ft
Elevation Range = 4,350 ft
Mean Elevation = 6,801 ft
China Mountain PWA has 488 acres of late seral forest or 4 % of the total area. In China Mountain PWA there are 6,621 acres of serpentine or 58 %. China Mountain PWA has the eighth most serpentine of the PWAs. Within China Mountain, PWA Natural Diversity Database has identified 24 state or global rank rare species occurrences, the seventh most occurrences of all the PWAs. They consist of 1 animal species, 13 plant species, 4 aquatic species, and 6 terrestrial communities. China Mountain PWA contains 2 threatened extremely endangered and 1 threatened rare Holland community types. It also contains 3 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Chinquapin Potential Wilderness Area
Shasta-Trinity National Forest
Size = 26,130 acres
Minimum Elevation = 2,336 ft
Maximum Elevation = 5,984 ft
Elevation Range = 3,648 ft
Mean Elevation = 3,740 ft
Chinquapin PWA along with South Fork Trinity PWA is important in supplying connectivity between Yolla Bolly Middle Eel PWA and the mainstem of the Trinity River. Chinquapin PWA has 12,991 acres of late seral forest or 50 % of the total area, the sixth largest late seral forest acreage of the PWAs. Salmonid species use a total of 22 miles of the streams, the eighth greatest amount of occupied salmonid habitat of the PWAs. In Chinquapin PWA there are 377 acres of serpentine or 1 %. 26,103 acres of Chinquapin PWA are located in a designated Northwest Forest Plan Key Watershed or 100 % of the total area. This PWA contains the sixth largest Key Watershed acreage of the PWAs. Within Chinquapin PWA, the Natural Diversity Database has identified 10 state or global ranked rare species occurrences consisting of 7 animal species, 2 plant species, and 1 terrestrial community. Chinquapin PWA contains 1 very threatened endangered Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Condrey Mountain Potential Wilderness Area
Klamath and Rogue River National Forests
Size = 14,840 acres
Minimum Elevation = 2,083 ft
Maximum Elevation = 7,093 ft
Elevation Range = 5,010 ft
Mean Elevation = 4,961 ft
Condrey Mountain PWA supplies connectivity between the Siskiyou Wilderness and the Siskiyou Crest. Condrey Mountain PWA has 5,968 acres of late seral forest or 40 % of the total area. Salmonid species use a total of 8 miles of the streams. In Condrey Mountain PWA there are 584 acres of serpentine or 4 %. The Natural Diversity Database has identified 12 occurrences of Califonia State or globally ranked rare species, the tenth most occurrences of all the PWAs. Within Condrey Mountain there are 4 animal species and 8 plant species. Condrey Mountain PWA contains 2 threatened extremely endangered, 1 very threatened endangered, and 1 threatened rare Holland community types. It also contains 3 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Deer Mountain Potential Wilderness Area
Mendocino National Forest
Size = 14,998 acres
Minimum Elevation = 886 ft
Maximum Elevation = 4,439 ft
Elevation Range = 3,553 ft
Mean Elevation = 2,642 ft
Deer Mountain PWA has 1,378 acres of late seral forest or 9 % of the total area. In Deer Mountain PWA there are 6,229 acres of serpentine or 42 %. Deer Mountain PWA has the tenth most serpentine of the PWAs. Deer Mountain PWA contains 1 non-ranked Holland community type. It also contains 4 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Devil’s Rock Potential Wilderness Area
Shasta Trinity National Forest
Size = 23,630 acres
Minimum Elevation = 1,066 ft
Maximum Elevation = 3,451 ft
Elevation Range = 2,385 ft
Mean Elevation = 1,843 ft
Devil’s Rock PWA has the fourth lowest mean elevation of the PWAs. Devil’s Rock PWA has 8,163 acres of late seral forest or 35% of the total area. The Natural Diversity Database has identified 13 occurrences of California State or globally ranked rare species, the eighth most occurrences of all the PWAs. They consist of 4 animal species, 5 invertebrate species, 1 plant species, and 3 aquatic species. Devil’s Rock PWA contains 1 threatened rare and 1 rare Holland community types. It also contains 7 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Donomore Peak Potential Wilderness Area
Rouge River National Forest
Size = 1,284 acres
Minimum Elevation = 3,839 ft
Maximum Elevation = 6,529 ft
Elevation Range = 2,690 ft
Mean Elevation = 5,206 ft
Donomore Peak PWA has 473 acres of late seral forest or 37% of the total area. In Donomore Peak PWA there are 20 acres of serpentine or 2%. Donomore Peak PWA contains 1 threatened extremely endangered and 1 threatened rare Holland community types. It also contains 2 types with less than 50% of its distribution represented in a protected area in California. They are listed below.
Eagle Potential Wilderness Area
Shasta Trinity National Forest
Size = 8,522 acres
Minimum Elevation = 1,250 ft
Maximum Elevation = 5,699 ft
Elevation Range = 4,449 ft
Mean Elevation = 3,056 ft
Eagle PWA has 4,275 acres of late seral forest, or 50% of the total area. Salmonid species use a total of 2 miles of the streams. In Eagle PWA there are 16 acres of serpentine. The Natural Diversity Database has identified 7 occurrences of California State or globally ranked rare species. They consist of 2 animal species and 5 invertebrate species. Eagle PWA contains 1 very threatened endangered and 1 rare Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
East Fork Mountain Potential Wilderness Area
Shasta Trinity National Forest
Size = 10,075 acres
Minimum Elevation = 1,450 ft
Maximum Elevation = 4,357 ft
Elevation Range = 2,907 ft
Mean Elevation = 2,470 ft
East Fork Mountain PWA has the tenth lowest mean elevation of the PWAs. East Fork Mountain PWA has 4,693 acres of late seral forest or 47% of the total area. The Natural Diversity Database has identified 1 occurrence of California State or globally ranked rare species, consisting of 1 animal species. East Fork Mountain PWA 1 rare Holland community type. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Fox Ridge Potential Wilderness Area
Six Rivers National Forest
Size = 5,311 acres
Minimum Elevation = 837 ft
Maximum Elevation = 4,078 ft
Elevation Range = 3,241 ft
Mean Elevation = 2,476 ft
Fox Ridge PWA has 1,064 acres of late seral forest or 20% of the total area. There are 1,459 acres of Port Orford cedar with 246 acres being infected with the root rot disease. Fox Ridge PWA has the sixth largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 6 miles of the streams. In Fox Ridge PWA there are 4,420 acres of serpentine or 83%. 5,311 acres of Fox Ridge PWA are located in a designated Northwest Forest Plan Key Watershed, or 100% of the total area. Fox Ridge PWA contains 1 threatened rare Holland community type. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Girard Ridge Potential Wilderness Area
Shasta Trinity National Forest
Size = 42,218 acres
Minimum Elevation = 1,188 ft
Maximum Elevation = 5,574 ft
Elevation Range = 4,386 ft
Mean Elevation = 3,330 ft
Girard Ridge PWA is the seventh largest of the PWAs. Girard Ridge PWA has 16,149 acres of late seral forest or 38% of the total area, the fifth largest late seral forest acreage of the PWAs. The Natural Diversity Database has identified 10 occurrences of California State or globally ranked rare species. They consist of 7 animal species and 1 plant species. Girard Ridge PWA contains 1 non-ranked Holland community types. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Grindstone Potential Wilderness Area
Mendocino National Forest
Size = 51,585 acres
Minimum Elevation = 761 ft
Maximum Elevation = 5,387 ft
Elevation Range = 4,626 ft
Mean Elevation = 2,988 ft
Grindstone PWA is the fifth largest of the PWAs. Grindstone PWA has 10,491 acres of late seral forest or 20% of the total area, the ninth largest late seral forest acreage of the PWAs. In Grindstone PWA there are 272 acres of serpentine or 1%. 18 acres of Grindstone PWA are located in a designated Northwest Forest Plan Key. The Natural Diversity Database has identified 4 occurrences of California State or globally ranked rare species. They consist of 4 animal species. Grindstone PWA contains 1 threatened rare and 2 rare Holland community types. It also contains 9 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Horse Mountain Potential Wilderness Area
Shasta-Trinity National Forest
Size = 12,737 acres
Minimum Elevation = 1,066 ft
Maximum Elevation = 4,334 ft
Elevation Range = 3,268 ft
Mean Elevation = 2,092 ft
Horse Mountain PWA has the fifth lowest mean elevation of the PWAs. Horse Mountain PWA has 3,154 acres of late seral forest or 25% of the total area and 61 acres of Permanently flooded Lacustrine Habitat. The Natural Diversity Database has identified 8 occurrences of California State or globally ranked rare species. They consist of 2 invertebrate species, 2 plant species, and 4 aquatic species. Horse Mountain PWA contains 1 very threatened endangered and 1 rare Holland community types. It also contains 7 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Kalmiopsis Potential Wilderness Area
Six Rivers National Forest
Size = 1,107 acres
Minimum Elevation = 876 ft
Maximum Elevation = 2,608 ft
Elevation Range = 1,732 ft
Mean Elevation = 1,670 ft
Kalmiopsis PWA has the third lowest mean elevation of the PWAs. Kalmiopsis PWA has 20 acres of late seral forest or 2% of the total area. There are 493 acres of Port Orford cedar with 65 acres being infected with the root rot disease. Kalmiopsis PWA has the ninth largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 1 mile of the streams. In Kalmiopsis PWA there are 1,092 acres of serpentine or 99%. 1,107 acres of Kalmiopsis PWA are located in a designated Northwest Forest Plan Key Watershed or 100% of the total area. The Natural Diversity Database has identified 1 occurrence of a California State or globally ranked rare species, consisting of 1 plant species (this seems really low – this is serpentine habitat – lots of endemics). Kalmiopsis PWA contains 1 threatened rare Holland community types. It also contains 2 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Kelly Peak Potential Wilderness Area
Six Rivers National Forest
Size = 5,636 acres
Minimum Elevation = 653 ft
Maximum Elevation = 3,845 ft
Elevation Range = 3,192 ft
Mean Elevation = 2,134 ft
Kelly Peak PWA has the sixth lowest mean elevation of the PWAs. Kelly Peak PWA has 1,005 acres of late seral forest, or 18% of the total area. There are 3,618 acres of Port Orford cedar with 11 acres being infected with the root rot disease. Kelly Peak PWA has the third largest acreage of non-diseased Port Orford Cedars of the PWAs. In Kelly Peak PWA there are 4,951 acres of serpentine or 88%. 5,636 acres of Kelly Peak PWA are located in a designated Northwest Forest Plan Key Watershed or 100% of the total area. The Natural Diversity Database has identified 3 occurrences of California State or globally ranked rare species. They consist of 1 animal species and 2 plant species. Kelly Peak PWA contains 1 threatened rare Holland community type. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Mad River Buttes Potential Wilderness Area
Six Rivers National Forest
Size = 6,511 acres
Minimum Elevation = 2,215 ft
Maximum Elevation = 5,269 ft
Elevation Range = 3,054 ft
Mean Elevation = 4,183 ft
Mad River Buttes PWA has 2,316 acres of late seral forest, or 36% of the total area. 43 acres of Mad River Buttes PWA are located in a designated Northwest Forest Plan Key Watershed or 1% of the total area. The Natural Diversity Database has identified 2 occurrences of California State or globally ranked rare species. They consist of 2 animal species. Mad River Buttes PWA contains 3 Holland community types with less than 25% and of its distribution represented in a protected area in California. They are listed below.
Marble Mountain Potential Wilderness Area
Klamath National Forest
Size = 135,562 acres
Minimum Elevation = 640 ft
Maximum Elevation = 7,520 ft
Elevation Range = 6,880 ft
Mean Elevation = 3,747 ft
Marble Mountain PWA is important in supplying connectivity between Marble Mountain Wilderness and Trinity Alps and Russian Wilderness areas. Marble Mountain PWA is the second largest and has the third greatest elevation range of the PWAs. Marble Mountain PWA has 35,889 acres of late seral forest, or 26% of the total area, the second largest late seral forest acreage of the PWAs. Salmonid species use a total of 38 miles of the streams, the third greatest amount of occupied salmonid habitat of the PWAs. In Marble Mountain PWA there are 8,284 acres of serpentine or 6%. Marble Mountain PWA has the fourth most serpentine of the PWAs. 84,012 acres of Marble Mountain PWA are located in a designated Northwest Forest Plan Key Watershed or 62% of the total area. This PWA contains the third largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 44 occurrences of California State or globally ranked rare species, the fourth most occurrences of all the PWAs.. They consist of 35 animal species, 5 plant species, 3 aquatic species, and 1 aquatic community. Marble Mountain PWA contains 2 threatened extremely endangered, 2 very threatened endangered, 2 rare, and 2 non-ranked Holland community types. It also contains 11 types with less than 25% and 5 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Mount Eddy Potential Wilderness Area
Shasta Trinity National Forest
Size = 18,224 acres
Minimum Elevation = 5,220 ft
Maximum Elevation = 8,999 ft
Elevation Range = 3,780 ft
Mean Elevation = 6,906 ft
Mount Eddy PWA has 444 acres of late seral forest or 2% of the total area. In Mount Eddy PWA there are 15,689 acres of serpentine or 86%. Mount Eddy PWA has the third most serpentine of the PWAs. The Natural Diversity Database has identified 48 occurrences of California State or globally ranked rare species, the second most occurrences of all the PWAs. They consist of 1 animal species, 33 plant species, and 11 aquatic species. Mount Eddy PWA contains 1 threatened extremely endangered, 1 very threatened endangered, and 1 rare Holland community types. It also contains 3 types with less than 25% and 5 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Mount Shasta Potential Wilderness Area
Shasta Trinity National Forest
Size = 6,152 acres
Minimum Elevation = 4,150 ft
Maximum Elevation = 11,982 ft
Elevation Range = 7,831 ft
Mean Elevation = 6,892 ft
Mount Shasta PWA has the greatest elevation range of the PWAs. Mount Shasta PWA has 278 acres of late seral forest or 5% of the total area. In Mount Shasta PWA there are N/A acres of serpentine. The Natural Diversity Database has identified 3 occurrences of California State or globally ranked rare species. They consist of 3 plant species. Mount Shasta PWA contains 2 very threatened endangered and 1 non-ranked Holland community types. It also contains 5 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Mt. Lassic Potential Wilderness Area
Six Rivers National Forest
Size = 10,487 acres
Minimum Elevation = 2,736 ft
Maximum Elevation = 5,883 ft
Elevation Range = 3,146 ft
Mean Elevation = 4,330 ft
Mt. Lassic PWA has 5,142 acres of late seral forest, or 49% of the total area. Salmonid species use a total of 5 miles of the streams. In Mt. Lassic PWA there are 2,179 acres of serpentine or 21%. The Natural Diversity Database has identified 4 occurrences of California State or globally ranked rare species. They consist of 1 animal species and 3 plant species. Mt. Lassic PWA contains 1 very threatened endangered, 2 threatened rare, and 1 rare Holland community types. It also contains 7 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
North Fork Eel Potential Wilderness Area
Bureau of Land Management and Six Rivers National Forest
Size = 20,979 acres
Minimum Elevation = 1,358 ft
Maximum Elevation = 4,531 ft
Elevation Range = 3,173 ft
Mean Elevation = 2,661 ft
North Fork Eel PWA has 3,898 acres of late seral forest or 19% of the total area. Salmonid species use a total of 14 miles of the streams. In North Fork Eel PWA there are 20 acres of serpentine. 20,469 acres of North Fork Eel PWA are located in a designated Northwest Forest Plan Key Watershed or 98% of the total area. This PWA contains the tenth largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 3 occurrences of California State or globally ranked rare species. They consist of 3 animal species. North Fork Eel PWA contains 2 threatened rare and 1 rare Holland community types. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
North Fork Smith Potential Wilderness Area
Six Rivers National Forest
Size = 38,189 acres
Minimum Elevation = 384 ft
Maximum Elevation = 3,743 ft
Elevation Range = 3,360 ft
Mean Elevation = 2,158 ft
North Fork Smith PWA is the tenth largest, and is the seventh lowest in mean elevation of the PWAs. North Fork Smith PWA has 1,223 acres of late seral forest or 3% of the total area. There are 15,014 acres of Port Orford cedar with 956 acres being infected with the root rot disease. North Fork Smith PWA has the second largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 26 miles of the streams, the seventh greatest amount of occupied salmonid habitat of the PWAs.. In North Fork Smith PWA there are 35,119 acres of serpentine or 92%. North Fork Smith PWA has the second most serpentine of the PWAs. 38,038 acres of North Fork Smith PWA are located in a designated Northwest Forest Plan Key Watershed or 100% of the total area. This PWA contains the fourth largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 40 occurrences of California State or globally ranked rare species, the fifth most occurrences of all the PWAs. They consist of 1 animal species, and 39 plant species. North Fork Smith PWA contains 1 very threatened rare and 2 threatened rare Holland community types. It also contains 7 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Panther Potential Wilderness Area
Shasta Trinity National Forest
Size = 13,405 acres
Minimum Elevation = 994 ft
Maximum Elevation = 5,210 ft
Elevation Range = 4,216 ft
Mean Elevation = 2,547 ft
Panther PWA has 4,054 acres of late seral forest, or 30% of the total area. The Natural Diversity Database has identified 7 occurrences of California State or globally ranked rare species. They consist of 7 animal species. Panther PWA contains 1 rare and 1 non-ranked Holland community types. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Pattison Potential Wilderness Area
Shasta Trinity National Forest
Size = 31,011 acres
Minimum Elevation = 1,260 ft
Maximum Elevation = 5,837 ft
Elevation Range = 4,577 ft
Mean Elevation = 3,096 ft
Pattison PWA has 11,344 acres of late seral forest, or 37% of the total area, the seventh largest late seral forest acreage of the PWAs. Salmonid species use a total of 31 miles of the streams, the fourth greatest amount of occupied salmonid habitat of the PWAs. In Pattison PWA there are 108 acres of serpentine. The Natural Diversity Database has identified 6 occurrences of California State or globally ranked rare species. They consist of 5 animal species and 1 plant species. Pattison PWA contains 1 very threatened endangered, 1 threatened rare, and 1 non-ranked Holland community types. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Red Buttes Potential Wilderness Area
Klamath and Rouge River National Forest
Size = 61,417 acres
Minimum Elevation = 1,266 ft
Maximum Elevation = 6,722 ft
Elevation Range = 5,456 ft
Mean Elevation = 3,787 ft
Red Buttes PWA supplies connectivity between the Marbled Mountain and Siskiyou Wilderness and the Siskiyou Crest. Red Buttes PWA is the fourth largest and has the ninth greatest elevation range of the PWAs. Red Buttes PWA has 11,300 acres of late seral forest, or 18% of the total area, the eighth largest late seral forest acreage of the PWAs. Salmonid species use a total of 28 miles of the streams, the fifth greatest amount of occupied salmonid habitat of the PWAs. In Red Buttes PWA there are 7,619 acres of serpentine or 12%. Red Buttes PWA has the seventh most serpentine of the PWAs. The Natural Diversity Database has identified 11 occurrences of California State or globally ranked rare species. They consist of 6 animal species, 4 plant species, and 1 aquatic species. Red Buttes PWA contains 1 threatened extremely endangered, 1 very threatened endangered, 1 very threatened rare,, 1 threatened rare, and 1 rare Holland community types. It also contains 12 types with less than 25% and 5 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Rowdy Creek Potential Wilderness Area
Six Rivers National Forest
Size = 5,364 acres
Minimum Elevation = 331 ft
Maximum Elevation = 2,480 ft
Elevation Range = 2,149 ft
Mean Elevation = 1,415 ft
Rowdy Creek PWA has the second lowest mean elevation of the PWAs. Rowdy Creek PWA has 968 acres of late seral forest, or 18% of the total area. There are 1,052 acres of Port Orford cedar with 0 acres being infected with the root rot disease. Rowdy Creek PWA has the seventh largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 2 miles of the streams. In Rowdy Creek PWA there are 1,816 acres of serpentine or 34%. 33 acres of Rowdy Creek PWA are located in a designated Northwest Forest Plan Key Watershed or 1% of the total area. The Natural Diversity Database has identified 5 occurrences of California State or globally ranked rare species. They consist of 1 animal species and 4 plant species. Rowdy Creek PWA contains 1 endangered, 1 threatened rare and 1 non-ranked Holland community types. It also contains 5 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Russian Potential Wilderness Area
Klamath National Forest
Size = 33,041 acres
Minimum Elevation = 2,418 ft
Maximum Elevation = 7,936 ft
Elevation Range = 5,518 ft
Mean Elevation = 5,248 ft
Russian PWA is important in supplying connectivity between Russian Wilderness and Marble Mountain and Trinity Alps Wilderness areas. It is also known for having the highest diversity of conifers in the world. Russian PWA has the seventh greatest elevation range of the PWAs. Russian PWA has 10,355 acres of late seral forest, or 31% of the total area, the tenth largest late seral forest acreage of the PWAs. Salmonid species use a total of 5 miles of the streams. 24,876 acres of Russian PWA are located in a designated Northwest Forest Plan Key Watershed, or 75% of the total area. This PWA contains the seventh largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 13 occurrences of California State or globally ranked rare species, the ninth most occurrences of all the PWAs. They consist of 10 animal species, 2 plant species, and 1 aquatic community. Russian PWA contains 1 threatened extremely endangered, 1 very threatened endangered, 1 threatened rare, and 1 rare Holland community types. It also contains 6 types with less than 25% and 4 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Sanhedrin Mountain Potential Wilderness Area
Mendocino National Forest
Size = 10,943 acres
Minimum Elevation = 1,647 ft
Maximum Elevation = 6,125 ft
Elevation Range = 4,478 ft
Mean Elevation = 3,889 ft
Sanhedrin Mountain PWA has 1,892 acres of late seral forest, or 17% of the total area. In Sanhedrin Mountain PWA there are 3 acres of serpentine. The Natural Diversity Database has identified 5 occurrences of California State or globally ranked rare species. They consist of 2 animal species and 3 plant species. Sanhedrin Mountain PWA contains 2 threatened rare and 1 rare Holland community types. It also contains 11 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Shelly Creek Potential Wilderness Area
Siskiyou and Six Rivers National Forest
Size = 8,675 acres
Minimum Elevation = 1,194 ft
Maximum Elevation = 3,842 ft
Elevation Range = 2,648 ft
Mean Elevation = 2,453 ft
Shelly Creek PWA has the ninth lowest mean elevation of the PWAs. Shelly Creek PWA has 2,475 acres of late seral forest, or 29% of the total area. There are 1,193 acres of Port Orford cedar with 359 acres being infected with the root rot disease. Shelly Creek PWA has the eighth largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 2 miles of the streams. In Shelly Creek PWA there are 382 acres of serpentine, or 4%. 6,922 acres of Shelly Creek PWA are located in a designated Northwest Forest Plan Key Watershed, or 80% of the total area. The Natural Diversity Database has identified 6 occurrences of California State or globally ranked rare species. They consist of 2 animal species, 3 plant species, and 1 aquatic species. Shelly Creek PWA contains 1 threatened rare Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Ship Mountain Potential Wilderness Area
Six rivers National Forest
Size = 9,642 acres
Minimum Elevation = 1,073 ft
Maximum Elevation = 5,305 ft
Elevation Range = 4,232 ft
Mean Elevation = 3,202 ft
Ship Mountain PWA has 1,521 acres of late seral forest, or 16% of the total area. There are 2,264 acres of Port Orford cedar with 0 acres infected with the root rot disease. Ship Mountain PWA has the fourth largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 4 miles of the streams. In Ship Mountain PWA there are 8,067 acres of serpentine, or 84%. Ship Mountain PWA has the sixth most serpentine of the PWAs. 9,642 acres of Ship Mountain PWA are located in a designated Northwest Forest Plan Key Watershed, or 100% of the total area. The Natural Diversity Database has identified 3 occurrences of California State or globally ranked rare species. They consist of 1 plant species and 2 aquatic species. Ship Mountain PWA contains 1 threatened rare Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Siskiyou Potential Wilderness Area
Klamath, Kiskiyou, and Six Rivers National Forest
Size = 135,162 acres
Minimum Elevation = 430 ft
Maximum Elevation = 6,270 ft
Elevation Range = 5,840 ft
Mean Elevation = 3,269 ft
Siskiyou PWA is the third largest and has the fourth greatest elevation range of the PWAs. Siskiyou PWA has 30,311 acres of late seral forest, or 22% of the total area, the third largest late seral forest acreage of the PWAs. There are 17,357 acres of Port Orford cedar with 46 acres being infected with the root rot disease. Siskiyou PWA has the largest acreage of non-diseased Port Orford Cedars of the PWAs. Salmonid species use a total of 46 miles of the streams, the second greatest amount of occupied salmonid habitat of the PWAs. In Siskiyou PWA there are 37,015 acres of serpentine, or 27%. Siskiyou PWA has the most serpentine of the PWAs. 105,836 acres of Siskiyou PWA are located in a designated Northwest Forest Plan Key Watershed, or 78% of the total area. This PWA contains the second largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 48 occurrences of California State or globally ranked rare species, the third most occurrences of all the PWAs. They consist of 27 animal species, 15 plant species, 4 aquatic species, and 2 terrestrial communities. Siskiyou PWA contains 2 threatened extremely endangered, 2 very threatened endangered, 1 very threatened rare, 2 threatened rare, 1 non-ranked Holland community types. It also contains 15 types with less than 25% and 6 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Snow Mountain Potential Wilderness Area
Mendocino National Forest
Size = 38,608 acres
Minimum Elevation = 1,257 ft
Maximum Elevation = 6,765 ft
Elevation Range = 5,509 ft
Mean Elevation = 3,308 ft
Snow Mountain PWA is the ninth largest and has the eighth greatest elevation range of the PWAs. Snow Mountain PWA has 9,165 acres of late seral forest, or 24 % of the total area. Salmonid species use a total of 7 miles of the streams. In Snow Mountain PWA there are 1,609 acres of serpentine, or 4 %. 16,287 acres of Snow Mountain PWA are located in a designated Northwest Forest Plan Key Watershed, or 42 % of the total area. The Natural Diversity Database has identified 2 occurrences of California State or globally ranked rare species consisting of 2 animal species. Snow Mountain PWA contains 1 very threatened endangered and 1 threatened rare Holland community types. It also contains 15 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Soda Mountain Potential Wilderness Area
Bureau of Land Management
Size = 10,709 acres
Minimum Elevation = 2,359 ft
Maximum Elevation = 4,600 ft
Elevation Range = 2,241 ft
Mean Elevation = 3,375 ft
Soda Mountain PWA is import for supplying connectivity to the Cascade-Siskiyou national monument and as a travel corridor to migration of the largest wintering herd of deer in southwest Oregon. Soda Mountain PWA has 173 acres of late seral forest, or 2 % of the total area. The Natural Diversity Database has identified two occurrences of California State or globally ranked rare species. They consist of one animal species and one plant species. Soda Mountain PWA contains 1 very threatened endangered and 1 rare Holland community types. It also contains 4 types with less than 25% of its distribution represented in a protected area in California. Oak woodlands and Oak grasslands are poorly represented in protected areas, particularly these which are valued because of the large size of the oaks and intact grasslands present in some of the areas that haven’t been intensively grazed. The Holland community types are listed below.
South Fork Trinity Potential Wilderness Area
Shasta Trinity National Forest
Size = 22,671 acres
Minimum Elevation = 1,417 ft
Maximum Elevation = 5,171 ft
Elevation Range = 3,753 ft
Mean Elevation = 3,036 ft
South Fork Trinity PWA has 7,058 acres of late seral forest, or 31 % of the total area. Salmonid species use a total of 26 miles of the streams, the sixth greatest amount of occupied salmonid habitat of the PWAs. In South Fork Trinity PWA there are 344 acres of serpentine. 22,671 acres of South Fork Trinity PWA are located in a designated Northwest Forest Plan Key Watershed, or 100 % of the total area. This PWA contains the ninth largest Key Watershed acreage of the PWAs. South Fork Trinity PWA along with Chinquapin PWA is important in supplying connectivity between Yolla Bolly Middle Eel PWA and the mainstem of the Trinity River. The Natural Diversity Database has identified 7 occurrences of California State or globally ranked rare species. They consist of 4 animal species and one plant species. South Fork Trinity PWA contains 1 very threatened endangered Holland community type. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Thomes Creek Potential Wilderness Area
Mendocino National Forest
Size = 20,117 acres
Minimum Elevation = 1,050 ft
Maximum Elevation = 5,157 ft
Elevation Range = 4,108 ft
Mean Elevation = 3,021 ft
Thomes Creek PWA has 4,472 acres of late seral forest, or 22 % of the total area. In Thomes Creek PWA there are 2,851 acres of serpentine, or 14 % of the total area. The Natural Diversity Database has identified 4 occurrences of California State or globally ranked rare species. They consist of 3 animal species and one plant species. Thomes Creek PWA contains 1 very threatened rare, 1 threatened rare, and 1 non-ranked Holland community types. It also contains 7 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Tom Martin Potential Wilderness Area
Klamath National Forest
Size = 16,611 acres
Minimum Elevation = 1,437 ft
Maximum Elevation = 6,991 ft
Elevation Range = 5,554 ft
Mean Elevation = 3,683 ft
Tom Martin PWA has the sixth greatest elevation range of the PWAs. Tom Martin PWA has 4,801 acres of late seral forest, or 29 % of the total area. Salmonid species use a total of one mile of the streams. In Tom Martin PWA there are 8,267 acres of serpentine, or 50% of the total area. Tom Martin PWA has the fifth most serpentine of the PWAs. The Natural Diversity Database has identified 4 occurrences of California State or globally ranked rare species. They consist of 3 animal species and one plant species. Tom Martin PWA contains 2 threatened extremely endangered, 1 very threatened endangered, 1 threatened rare, and 1 non-ranked Holland community types. It also contains 7 types with less than 25% and 3 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Trinity Alps Potential Wilderness Area
Klamath, Shasta-Trinity, Six Rivers National Forests and Bureau of Land Management
Size = 170,055 acres
Minimum Elevation = 479 ft
Maximum Elevation = 7,451 ft
Elevation Range = 6,972 ft
Mean Elevation = 3,341 ft
Trinity Alps PWA is important in supplying connectivity between Trinity Alps Wilderness and Marble Mountain and Russian Wilderness areas. Trinity Alps PWA is the largest and has the second greatest elevation range of the PWAs. Trinity Alps PWA has 52,906 acres of late seral forest, or 31 % of the total area, the largest late seral forest acreage of the PWAs. Salmonid species use a total of 63 miles of the streams, the greatest amount of occupied salmonid habitat of the PWAs. In Trinity Alps PWA there are 1,539 acres of serpentine, or 1% of the total area. 131,947 acres of Trinity Alps PWA are located in a designated Northwest Forest Plan Key Watershed, or 78 % of the total area. This PWA contains the largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 66 occurrences of California State or globally ranked rare species, the most occurrences of all the PWAs. They consist of 53 animal species, 2 invertebrate species, 2 plant species, 6 aquatic species, and 3 aquatic communities. Trinity Alps PWA contains 1 threatened extremely endangered, 1 very threatened endangered, 2 threatened rare, 1 rare, and 2 non-ranked Holland community types. It also contains 17 types with less than 25% and 2 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Underwood Potential Wilderness Area
Six Rivers and Shasta Trinity National Forest
Size = 16,127 acres
Minimum Elevation = 656 ft
Maximum Elevation = 4,902 ft
Elevation Range = 4,245 ft
Mean Elevation = 2,690 ft
Underwood PWA has 5,618 acres of late seral forest, or 35 % of the total area. Salmonid species use a total of 8 miles of the streams. In Underwood PWA there are 755 acres of serpentine, or 5 %. 10,800 acres of Underwood PWA are located in a designated Northwest Forest Plan Key Watershed, or 67 % of the total area. The Natural Diversity Database has identified 10 occurrences of California State or globally ranked rare species consisting of 10 animal species. Underwood PWA contains 1 rare Holland community types. It also contains 6 types with less than 25% of its distribution represented in a protected area in California. They are listed below.
Yolla Bolly Middle Eel Potential Wilderness Area
Mendocino, Shasta Trinity, Six Rivers National Forests and Bureau of Land Management
Size = 47,946 acres
Minimum Elevation = 1,555 ft
Maximum Elevation = 7,329 ft
Elevation Range = 5,774 ft
Mean Elevation = 4,453 ft
Yolla Bolly Middle Eel PWA is the sixth largest and has the fifth greatest elevation range of the PWAs. Yolla Bolly Middle Eel PWA has 19,475 acres of late seral forest, or 41 % of the total area, the fourth largest late seral forest acreage of the PWAs. Salmonid species use a total of 18 miles of the streams, the ninth greatest amount of occupied salmonid habitat of the PWAs. In Yolla Bolly Middle Eel PWA there are 71 acres of serpentine. 34,433 acres of Yolla Bolly Middle Eel PWA are located in a designated Northwest Forest Plan Key Watershed, or 72 % of the total area. This PWA contains the fifth largest Key Watershed acreage of the PWAs. The Natural Diversity Database has identified 24 occurrences of California State or globally ranked rare species, the sixth most occurrences of all the PWAs. They consist of 13 animal species, 6 plant species, 4 aquatic species, and 1 aquatic community. Yolla Bolly Middle Eel PWA contains 3 threatened rare and 1 rare Holland community types. It also contains 9 types with less than 25% and 1 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Yuki Potential Wilderness Area
Mendocino National Forest and Bureau of Land Management
Size = 38,608 acres
Minimum Elevation = 1,378 ft
Maximum Elevation = 6,529 ft
Elevation Range = 5,151 ft
Mean Elevation = 3,793 ft
Yuki PWA is the eighth largest and has the tenth greatest elevation range of the PWAs. Yuki PWA has 9,165 acres of late seral forest, or 24 % of the total area. Salmonid species use a total of 7 miles of the streams. In Yuki PWA there are 1,609 acres of serpentine, or 4 %. 16,287 acres of Yuki PWA are located in a designated Northwest Forest Plan Key Watershed, or 42 % of the total area. The Natural Diversity Database has identified 2 occurrences of California State or globally ranked rare species consisting of 2 animal species. Yuki PWA contains 2 threatened rare and 1 rare Holland community types. It also contains 11 types with less than 25% and 4 with less than 50% of its distribution represented in a protected area in California. They are listed below.
Discussion
The results of this assessment show in detail how each PWA contributes the regional reserve system for the Klamath-Siskiyou. All the PWAs do not contain all the variables analyzed; therefore the results quantify the variables that exist within each PWA. The purpose of this assessment was to determine the contribution each PWA makes to the regional reserve system, not to compare one PWA to another. Caution must be advised when trying to compare and contrast results between different PWAs, as the variable in question may not naturally exist across the full range of the study area.
Including these PWAs into the wilderness legislation will add to the reserve system of the Klamath-Siskiyou in a positive manner, by protecting special elements, under-represented vegetation community types, and the ecological processes. In turn helping to preserve the biological diversity of the ecoregion.
Special Elements
Late-seral old growth forest (LSOG) is an important component of a reserve system in the Klamath-Siskiyou (Strittholt et al. 1999, DellaSala et al. 1999). These forests supply unique habitat to a host of obligate species some of which are rare, threatened, endangered, sensitive, or of special concern. Late-seral forests may even include many soil microbes and microrihzal fungi that have not yet been discovered by science (Noss 2000). Such forests help supply cool water for salmonid species and other aquatic organisms, as well as for downstream users such as fish, agriculture, and urban populations. They also help to keep sediment from entering streams and rivers by inhibiting mass wasting and erosion, while also supplying large down woody debris for instream structure, a primary component of salmonid habitat. Late-seral forest stands are also more resistant to disturbances such as fire and insect infestations than younger forests and can recover from these stochastic events faster than younger forests (DellaSala et al. 1995, DellaSala and Frost 2001). The top 10 PWA for LSOG are:
Salmonid bearing streams are also a valuable resource to protect in the region as populations of most salmonid species in California are listed as threatened or endangered (National Marine Fisheries Service, 2002). As part of the 1994 Northwest Forest Plan Process, existing watersheds with high quality aquatic habitat were chosen to be "key watersheds." These watersheds were chosen to protect areas with intact aquatic ecosystems as refugia for salmonids and other aquatic species. PWAs in key watershed, being both roadless and important to aquatic species, are the best refugia for these species and are especially important in the roll of recovering salmonid species. The top 1o PWAs for salmon are:
Port Orford cedar (POC) is another important component of a reserve system for the Klamath-Siskiyou (Strittholt et al. 1999, DellaSala et al. 1999). Due to a devastating outbreak of a water-born root rot fungus (Phytophthora lateralis), which attacks POC and threatens the functional importance of the species, it is important to protect as much non-infected POC as possible. This would be especially true for roadless areas, where POC is still somewhat insulated from the fungus spreading by way of humans and motor vehicles (Strittholt and DellaSala 2001). Mud from infected areas contains spores of the deadly fungus, which can be picked up and spread via motor vehicles, bike tires, and boots. Once spread to uninfected areas, the fungus travels down hill infecting other areas. This demonstrates the importance of closing roads up slope from existing non-infected POC stands, and including PWAs with these stands in the wilderness legislation. Inclusion of PWAs that contain POC in the legislation may help save this species from extirpation and eventual extinction. The top 9 PWAs for POC are:
Including PWAs, which contain habitat for species, which are rare, threatened, endangered, or of special concern is critical in designing a reserve system. This assessment used EOs from the CNDDB to determine which PWAs contained locations of these species. These areas are known as biodiversity "hot spots" and are important for maintaining a full range of all native species in the Klamath-Siskiyou ecoregion. Although there were not many EOs found within the PWAs we believe this is more due to the lack of survey effort, than to the EOs not being there. A more inclusive analysis using finer scale and more complete information is needed to determine how the PWAs contribute to these species in terms of their habitat needs. The top 10 PWAs for rare species are:
Another important element to the Klamath-Siskiyou is its serpentine geology. Soil developed from serpentine rock is high in heavy metals and creates a harsh growing environment for plants. Because of this many rare plant and community types have evolved to grow in serpentinic soils. Since finer scale data for rare plants does not exist for the entire study area, inclusion of PWAs with serpentine, in wilderness legislation, may help protect many rare plant and community types that are highly correlated with these soil types. DellaSala et al. (1999), for instance, document the importance of serpentine soils, particularly those on the Siskiyou National Forest, as "hot spots" for rare and endemic plants, including many that are listed as threatened or sensitive by state or federal agencies. The top 10 PWAs for serpentine are:
Representation
The GAP has analyzed each Holland vegetation community type to determine its rarity and level of protection by calculating how much of the species is currently protected in a protected area. It is important to include in the wilderness legislation, PWAs which contain Holland types that are rare and or under-represented in the current reserve system. This will help satisfy the conservation goal of representing all native species across their natural range.
When considering the goal of representation, it is also important to look at elevation. Because of the predominance of higher elevation areas in the current wilderness system, lower elevation community types are under represented and are therefore, important to include in a reserve network. Mean elevation gives an approximation of the elevation of the overall area, but does not describe the differences of elevation within the PWA. PWAs with greater elevation ranges may potentially have a greater number of vegetation community types. By including in the legislation, lower elevation PWAs and those with greater elevation ranges, the amount of vegetation types that are under-represented in current protected areas will decrease. The 10 PWAs with the lowest mean elevations are:
Ecosystem Process
The size of a PWA is another important factor to consider when designing a reserve system. Larger protected areas are more capable than smaller protected areas in absorbing and maintaining ecological process (i.e. population regulation and fire -an important ecological process in the Klamath-Siskiyou). These larger PWAs are also important to area dependant species (such as large carnivores), which require large areas of high quality habitat. When evaluating size of a PWA it is important to take into consideration the location of the PWA in relation to other PWAs and existing wilderness areas. If the PWA is smaller but adjacent to or in close proximity to another PWA or wilderness area, it may supply as much conservation value (in terms of size) to the reserve system as a larger PWA, which is more isolated. Building from and connecting together existing wilderness areas is of primary importance when designing a reserve system. And would help to tie together the existing wilderness areas into a more connected and complete reserve system for the Klamath-Siskiyou. The 10 largest PWAs are:
Elevation gradients also play an important roll in maintaining intact ecosystem processes. This is important because elevation gradients allow for vegetation communities and individual plant species to adjust to global climatic change. Where a species would have to migrate hundreds of miles moving horizontally north and south to maintain the same climate, a large elevation gradient allows an opportunity for migration only hundreds of feet vertically to achieve the same results. The 10 PWAs with the largest elevation gradients are:
Conclusion
Including the Klamath-Siskiyou PWAs into the wilderness system will greatly contribute to the reserve system of the ecoregion as noted by the earlier work of researchers on reserve design (Strittholt et al. 1999, Noss et al. 1999, Strittholt and DellaSala 2001). Special elements such as late-seral forests, POC, serpentine geology, salmon, and other important species would be afforded increased protection. Rare and under-represented vegetation community types will gain representation in protected areas. Because the PWAs form land bridges and linkages between existing wilderness areas, natural processes such as fire, predation, pollination, and migration may remain functional thereby maintaining the biodiversity of the region. The amount of increased protection the region would receive if the PWAs were designated, as wilderness, is vital in protecting the biodiversity of the Klamath-Siskiyou ecoregion.
We identified a range of ecological attributes documenting the importance of each PWA. PWAs varied in importance regarding their importance in special element occurrences, salmon habitat, representation, and adjacency (i.e., connectivity) to existing wilderness areas. The protection of all 48 PWAs would complement the existing wilderness areas in a way that establishes a reserve network based on fundamental principles in reserve design and conservation biology.
Future Work
For
a more complete picture of the contribution the PWAs have to a reserve system, a more thorough analysis is recommended. First, the data gaps in this assessment need to be identified (i.e. lack of detail species data for PWAs in the CNDDB), and additional data layers gathered. Examples of additional data layers that may be available are: Condor areas, Bald and Golden eagle areas, Peregrine falcon areas, Goshawk nest and groves, Survey and manage species, Marbled Murrelet areas, Northern Spotted Owl (NSO) locations, critical plant habitat areas, threatened and endangered reptile habitat, Big Horn Sheep areas, Fisher predictability, NSO predictability, California Native Plant Society electronic database, special interest areas, National Recreation Area, wild and scenic rivers, archaeological areas, botanical areas, geological areas, historic areas, scenic areas, zoological areas, research natural areas, game refuge and preserves, and late seral reserves. Once the additional data layers are identified and gathered the PWAs can be analyzed using more specific information for species and variables of conservation interest. If a larger region other than the Klamath-Siskiyou is analyzed, care will have to be taken when determining the extent of the data gaps to be consistent with the variables and there geographic ranges.Literature Cited
DellaSala, D.A., D.M. Olson, S. Barth, S. Crane, and S. Primm. 1995. Forest health: getting beyond the rhetoric to restore healthy landscapes in the Inland Northwest. Wildlife Soc. Bull. 23(3): 346-356.
DellaSala, D.A., S.B. Reid, T.J. Frest, J.R. Strittholt, and D.M. Olson. 1999. A global perspective on the biodiversity of the Klamath-Siskiyou ecoregion. Natural Areas Journal 19:300-319.
DellaSala, D.A., and E. Frost. 2001. An ecologically based strategy for fire and fuels management in National Forest roadless areas. Fire Management Today 61(2): 12-23.
Keeler-Wolf, T. 1993. Conserving California’s Rare Plant Communities. Fremontia 22:14-22.
National Marine Fisheries Northwest Regional Office. 2002. Summary of Salmon and Steelhead listings. Accessed 26 March 2002 at: http://www.nwr.noaa.gov/1salmon/salmesa/pubs/1pgr.pdf
Noss, R.F., J.R. Strittholt, K. Vance-Borland, C. Carroll, and P. Frost. 1999. A conservation plan for the Klamath-Siskiyou ecoregion. Natural Areas Journal 19(4):392-411.
Noss, R.F. 2000. The Redwood Forest: History, Ecology, and Conservation of the Coast Redwoods. Island Press. Washington, D.C.
Strittholt, J.R., R.F. Noss, P.A. Frost, K. Vance-Borland, C. Carrol, and
G. Heilman. 1999. A conservation assessment and science-based plan for the
Klamath-Siskiyou ecoregion. Conservation Biology Institute, Corvallis, OR.
113 pp.
Strittholt, J.R., D.A. Dellasala. 2001. Importance of Roadless Area’s in Biodiversity Conservation in Forested Ecosystems: Case Study of the Klamath-Siskiyou Ecoregion of the United States. Conservation Biology 15:1742-1754.
Trombulak, S.C., C.A. Frissell. 2000. Review of Ecological Effects of Roads on Terrestrial and Aquatic Communities. Conservation Biology 14:18-30.
Appendix A. Geographic Information System data layers used in the ecological assessment.
|
THEME |
SCALE |
SOURCE |
|
Potential Wilderness Area’s |
1:24,000 |
Legacy – The Landscape Connection, 2001 |
|
Heritage Elements |
1:24,000 |
California Natural Diversity Database, California Department of Fish and Game, October 1, 2001. |
|
Salmonid Presence |
1:24,000 |
Klamath National Forest, 2000 Mendocino National Forest, 1997 Rogue River National Forest, Unknown Shasta-Trinity National Forest, 1997 Six Rivers National Forest, 1997 |
|
Serpentine Geology |
Mostly 1:24,000 (varies from 4,000 – 250,000) |
Klamath National Forest, 2001 |
|
Port-Orford-Cedar |
Unknown |
Six Rivers National Forest, Unknown |
|
Late Seral Forests |
30 meter |
Klamath Bioregional Assessment Project, Humboldt State University, 1994 |
|
Key Watersheds |
Unknown |
Regional Ecosystem Office, 1994 |
|
Elevation – Digital Elevation Model |
30 meter |
U.S. Geological Survey |
|
Holland Vegetation Types |
1:100,000 |
California Gap Analysis Project, 1998 |
Appendix B. Holland community types with state rarity rankings status and current percent representation for California.
|
CNDDB Community Type (Holland) |
CNDDB Rating |
Status 1&2 (% in CA) |
Status 1 (% in CA) |
Status 2 (% in CA) |
Status 3 (% in CA) |
Status 4 (% in CA) |
|
Alluvial Redwood Forest |
NR |
5 |
1 |
4 |
8 |
87 |
|
Black Oak Forest |
S4 |
8 |
6 |
2 |
45 |
47 |
|
Black Oak Woodland |
S3.2 |
5 |
3 |
2 |
37 |
59 |
|
Blue Oak Woodland |
S3.2 |
4 |
2 |
2 |
10 |
86 |
|
Bush Chinquapin Chaparral |
S3.3 |
20 |
19 |
1 |
56 |
24 |
|
Canyon Live Oak Forest |
S4 |
22 |
18 |
4 |
42 |
36 |
|
Cercocarpus ledifolius Woodland * |
-- |
15 |
12 |
3 |
76 |
9 |
|
Chamise Chaparral |
S4 |
13 |
11 |
2 |
29 |
57 |
|
Coast Range Mixed Coniferous Forest |
S4 |
15 |
12 |
3 |
48 |
37 |
|
Coast Range Ponderosa Pine Forest |
NR |
23 |
7 |
16 |
32 |
46 |
|
Eastside Ponderosa Pine Forest |
S2.1 |
3 |
2 |
1 |
67 |
31 |
|
Foothill Pine-Oak Woodland |
S4 |
3 |
1 |
2 |
13 |
83 |
|
Great Basin Mixed Scrub |
S4 |
8 |
5 |
3 |
70 |
22 |
|
Great Basin Woodlands |
11 |
9 |
2 |
64 |
25 |
|
|
Huckleberry Oak Chaparral |
S3.3 |
38 |
38 |
0 |
41 |
21 |
|
Interior Live Oak Forest |
S4 |
4 |
2 |
2 |
16 |
81 |
|
Jeffrey Pine Forest |
S4 |
22 |
20 |
2 |
67 |
11 |
|
Jeffrey Pine-Fir Forest |
S4 |
30 |
29 |
1 |
58 |
12 |
|
Klamath-Cascade Fell-field |
S4 |
95 |
95 |
0 |
4 |
1 |
|
Knobcone Pine Forest |
S4 |
3 |
2 |
1 |
60 |
36 |
|
Lodgepole Pine Forest |
S4 |
70 |
69 |
1 |
26 |
5 |
|
Mesic North Slope Chaparral |
-- |
29 |
25 |
4 |
42 |
28 |
|
Mixed Evergreen Forest |
S4 |
15 |
9 |
6 |
21 |
65 |
|
Mixed Montane Chaparral |
S4 |
26 |
24 |
2 |
52 |
22 |
|
Mixed North Slope Cismontane Woodland |
S3.2 |
2 |
1 |
1 |
20 |
79 |
|
Mixed Serpentine Chaparral |
1 |
0 |
1 |
34 |
66 |
|
|
Montane Ceanothus Chaparral |
-- |
14 |
12 |
2 |
51 |
35 |
|
Montane Meadow |
S3.2 |
27 |
26 |
1 |
30 |
44 |
|
Non-Native Grassland |
S4 |
5 |
1 |
4 |
7 |
88 |
|
Non-Serpentine Foothill Pine Woodland |
S4 |
8 |
5 |
3 |
32 |
60 |
|
North Coast Black Cottonwood Riparian Forest |
S1.1 |
1 |
0 |
1 |
40 |
59 |
|
North Coast Riparian Scrub |
S3.2 |
4 |
1 |
3 |
8 |
88 |
|
Northern Mixed Chaparral |
S4 |
8 |
6 |
2 |
44 |
48 |
|
Northern Ultramafic Jeffrey Pine Forest |
S3.2 |
24 |
24 |
0 |
52 |
24 |
|
Open Foothill Pine Woodland |
S4 |
11 |
7 |
4 |
21 |
68 |
|
Oregon Oak Woodland |
S3.3 |
3 |
2 |
1 |
32 |
66 |
|
Port Orford Cedar Forest |
S2.1 |
88 |
88 |
0 |
11 |
1 |
|
Red Fir Forest |
S4 |
48 |
47 |
1 |
42 |
10 |
|
Salmon-Scott Enriched Coniferous Forest |
S1.2 |
55 |
55 |
0 |
32 |
13 |
|
Scrub Oak Chaparral |
S3.3 |
24 |
23 |
1 |
50 |
27 |
|
Serpentine Foothill Pine-Chaparral Woodland |
S3.2 |
3 |
1 |
2 |
41 |
56 |
|
Shin Oak Brush |
S3.3 |
16 |
11 |
5 |
48 |
36 |
|
Sierran Mixed Coniferous Forest |
S4 |
9 |
8 |
1 |
49 |
42 |
|
Sierran White Fir Forest |
S4 |
23 |
22 |
1 |
52 |
25 |
|
Siskyou Enriched Coniferous Forest |
S1.2 |
44 |
44 |
0 |
49 |
7 |
|
Tan-Oak Forest |
S4 |
7 |
6 |
1 |
35 |
58 |
|
Ultramafic Mixed Coniferous Forest |
S4 |
16 |
7 |
9 |
74 |
10 |
|
Upland Douglas-Fir Forest |
S3.1 |
17 |
13 |
4 |
15 |
68 |
|
Upland Redwood Forest |
S2.3 |
13 |
5 |
8 |
5 |
83 |
|
Westside Ponderosa Pine Forest |
S2.1 |
14 |
13 |
1 |
46 |
40 |
|
Whitebark Pine Forest |
S4 |
61 |
59 |
2 |
39 |
1 |
California state rarity rankings:
S1 = extremely endangered: < 6 viable EO's or < 1,000 individuals, or < 2,000 acres of occupied habitat.
S2 = endangered: about 6-20 EO's, or 1,00 - 3,000 individual, or 2,000-10,000 acres of occupied habitat.
S3 = restricted range, rare: about 21 - 100 EO's, or 3,000 - 10,000 individuals, or 10,000 - 50,000 acres.
S4 = apparently secure: some factor exists to cause some concern such as narrow habitat or continuing threats.
S5 = demonstratably secure: commonly found throughout its historic range.
Threat ranks: