National interest in roadless area conservation dates back to the 1970s when the Forest Service was directed by Congress to inventory roadless areas in response to the public’s growing desire to protect wild landscapes primarily through wilderness designations. In 2001, President Clinton enacted the Roadless Conservation Rule to protect 58.5 million acres of inventoried roadless areas on Forest Service lands, including nearly 2 million acres in Oregon. However, on May 13, 2005 the Bush administration issued a revised rule that established a process for governors to propose locally supported regulations for conserving roadless area within their states. While some states, including Oregon, have legally challenged this rule change, State governments will continue to play a vital role in providing recommendations to the Forest Service concerning the protection of federal roadless areas. This report provides new information on the importance of roadless areas in Oregon that places these areas among the most ecologically valued in the nation, thereby providing a scientific foundation for protecting all of Oregon’s roadless lands regardless of the method to achieve this outcome.
The Peninsular Ranges extend 1,500 km (900 mi) from Southern California to the southern tip of the Baja California peninsula, forming a granitic spine near the western edge of the North American continent. They comprise an intact and rugged wilderness area connecting two countries and some of the richest montane and desert ecosystems in the world that support wideranging, iconic species, including mountain lion, California condor, and bighorn sheep. Connectivity at this continental scale is critical to maintaining ecosystem processes, biodiversity, wildlife movement, and habitat values of existing conservation investments in both countries.
This study was undertaken as part of a larger effort to conserve the integrity of this landscape linkage, in the face of increasing sprawl of development inland from the coast, escalating border security infrastructure, and other competing uses for the land. It focuses on the border region of California and Baja California, where the long-term connectivity between federally endangered bighorn sheep in Peninsular Ranges of Southern California and bighorn sheep in Baja California is threatened. The current level of connectivity and the possibilities for maintaining this connectivity in the future are not well understood. This preliminary study assesses the distribution and habitats of bighorn sheep in the Sierra Juárez in Baja California, just south of the international border, the potential threats to bighorn sheep there, and the threats to this landscape linkage, so as to inform conservation and management strategies for linking protected parklands in both countries.
The Global 200 Strategy amitiously seeks to conserve the variety of species, ecosystems, and ecological and evolutionary processes that sustain life on earth. Toward this end, the World Wildlife Fund hs identified over 200 ecoregions (Global 200) recognized for their high conservation priority, and calls for concentrated conservation planning in these regions. Not surprisingly, of the wide array of ecosystem types included in the Global 200, forest ecosystems constitute the majority. In fact, 87 of the 136 terrestrial ecoregions fall into one of five Major Habitat Types – Tropical and Subtropical Moist Brodleaf Forests, Tropical Dry Forests, Tropical and Sustropical Conifer Forests, Temperate Conifer and Broadleaf Forests, and Boreal Forests and Taiga.
The purpose of this report is threefold: (1) discuss the concept of forest restoration from a conservation biology perspective; (2) outline the ecological characteristics, technical constraints, socio-political and economic influences, and overall restoration principles relevant to the Global 200 major habitat types and associated realms; and (3) place forest restoration within the larger context of worldwide forest conservation.
The critically endangered Pacific pocket mouse (Perognathus longimembris pacificus), feared extinct for over 20 years, was “rediscovered” in 1993 and is now documented at four sites in Orange and San Diego Counties, California. Only one of these sites is considered large enough to be potentially self-sustaining without active intervention. In 1998, I gathered a team of biologists to initiate several research tasks in support of recovery planning for the species. The PPM Studies Team quickly determined that species recovery would require active translocations or reintroductions to establish new populations, but that we knew too little about the biology of P. l. pacificus and the availability of translocation receiver sites to design such a program. Recovery research from 1998 to 2000 therefore focused on (1) a systematic search for potential translocation receiver sites; (2) laboratory and field studies on non-listed, surrogate subspecies (P. l. longimembris and P. l. bangsi) to gain biological insights and perfect study methods; (3) studies on the historic and extant genetic diversity of P. l. pacificus; and (4) experimental habitat manipulations to increase P. l. pacificus populations. Using existing geographic information system (GIS) data, we identified sites throughout the historic range that might have appropriate soils and vegetation to support translocated P. l. pacificus. Reconnaissance surveys of habitat value were completed in all large areas of potential habitat identified by the model. Those sites having the highest habitat potential are being studied with more detailed and quantitative field analyses. The surrogate studies helped us design individual marking and monitoring methods and will be used to test translocation methods before applying them to P. l. pacificus. Genetic results suggest that P. l. pacificus populations were naturally fairly isolated from one another prior to modern development, that genetic diversity will continue to erode in the small populations that remain, and that individuals from extant populations could probably be mixed if maximizing genetic diversity in any newly established populations is an important recovery goal. Local populations should be increased in situ before they can supply donor animals for translocations. Experimental habitat management (shrub thinning) at one occupied site yielded a short-term, positive, behavioral response of mice to thinned habitat plots. However, the overall population seems to be in decline, and long-term population responses to habitat manipulations are not yet evident. The approach of the PPM Study Team has been to proceed cautiously and scientifically to obtain critical information and to design a translocation program, but we are prepared to recommend swift action to prevent extinction despite “insufficient data.” At this point, political and economic obstacles to species recovery seem larger than obstacles presented by scientific uncertainty.
Spencer, W.D. 2005. Recovery research for the endangered Pacific pocket mouse: An overview of collaborative studies. In B.E. Kus and J.L. Beyers, technical coordinators. Planning for Biodiversity: Bringing Research and Management Together: Proceedings of a Symposium for the South Coast Ecoregion. Gen. Tech. Rep. PSW-GTR-195. Pacific Southwest Research Station, Forest Service, U.S. Department of Agriculture, Albany, CA: 274pp.
Tejon Ranch is one of California’s most precious natural areas—a haven for rare and endangered species, a sanctuary for the soul of ancient California, a treasure that, through the years, has not escaped the wonderment of ranchers, hunters, wildlife enthusiasts, and scientists. This is a place through which thousands of people drive daily, but few have really seen; where one can visualize the dramatic geologic processes that shaped California’s landscape and influenced the evolutionary history of California’s diverse flora and fauna. In this place, California condors still fly, centuries-old oaks still flourish, and streams are born. Perhaps most remarkably, virtues of this place have not yet been compromised by the urban sprawl that is rapidly devouring so much of California’s natural landscape.
Tejon Ranch, 270,000 acres of southern Kern and northern Los Angeles counties, is the largest, contiguous, privately owned property in California. Owners of the Ranch are currently planning large-scale residential and industrial developments in what is now a largely undeveloped and natural landscape. Concerned that these development plans might severely compromise the Ranch’s ecological integrity before the public has had an opportunity to understand its significance, Environment Now and a coalition of environmental groups commissioned the Conservation Biology Institute to assess the regional and statewide value of Tejon Ranch for conservation of biological diversity. Through the course of this assessment, we have come to recognize what others have already suggested—that Tejon Ranch is truly one of California’s most priceless natural areas, unparalleled in its diversity of natural resources and its importance to conservation, and meeting all of the State’s criteria for a priority conservation target.
This report shares our synthesis of publicly available information—documenting the biogeographic importance of the Tejon Ranch region, revealing the values of the region’s natural resources, and identifying factors that threaten these values. This report does not advocate any specific open space design, but rather it illuminates the extraordinary values and regionally under-protected resources of the Ranch so that the public and decision-makers are fully aware of their importance in future land planning decisions. We hope that this information will be used as a basis for comprehensive, rather than piecemeal, land use planning of Tejon Ranch.
Tejon Ranch supports a multitude of irreplaceable biological resources, and the melding of these resources in one large, intact landscape makes the Ranch a regionally significant conservation target. This report evaluates the distribution of conservation values on Tejon Ranch, as an incremental step towards developing a regional reserve design.
We used publicly available data and science-based conservation principles to describe and map selected conservation values for Tejon Ranch. Our assessment demonstrates that, although different areas of the Ranch support different sets of conservation values, virtually all areas of the Ranch support one or more sets of values. To spatially describe the distribution of these values on Tejon Ranch, we identified four landscape units that differentially support the conservation values considered in our analysis:
- Lowland grasslands and oak savannas of the San Joaquin Valley (108,244 acres)
- Closed-canopy oak woodland, montane hardwood, and montane hardwood-conifer communities on the northwest slope of the Tehachapi Mountains (81,836 acres)
- Oak woodland, chaparral, and pinyon-juniper communities on the southeast slope of the Tehachapi Mountains (26,518 acres)
- Lowland Joshua tree woodland, grassland, and desert scrub communities of the Mojave Desert (53,613 acres)
Reserve designs for Tejon Ranch must, at a minimum, capture these values while ensuring the maintenance and management of ecological processes within and between landscape units. Similarly, conservation planning must ensure integration and connection of these landscape units with others in the region, along with a regional plan for long-term management and biological monitoring. Without careful and comprehensive consideration, land use plans for Tejon Ranch could irretrievably alter the biological functions and values of this keystone landscape.
CBI staff facilitated and contributed to several indepent science adivsory processes and recommendation reports for the Sacramento-San Joaquin Bay Delta Conservation Plan.
Bay Delta Conservation Plan, Aquatic
A group of nine scientists were convened in September 2007 to provide independent advice to the Bay Delta Conservation Plan (BDCP) Steering Committee. These scientists provided advice on the use of science in developing an effective Conservation Plan for the Sacramento-San Joaquin Delta in accordance with California’s Natural Community Conservation Planning Act (NCCPA) and the BDCP Planning Agreement. Consistent with the requirements of the NCCPA, the Science Advisors’ report includes a listing of principles for conservation planning, design, and management. The Report also includes a series of more specific recommendations regarding application of the existing knowledge base and the use of data and analyses for informing the BDCP. The following briefly summarizes key foundational principles and recommendations from the Report. These principles and recommendations should be considered as the overall conservation strategy and potential conservation measures are developed for the BDCP.
Bay Delta Conservation Plan, Aquatic (2007) PDF
Bay Delta Conservation Plan, Non-Aquatic
This report summarized recommendations from a group of six independent science advisors (ISA) concerning the treatment of non-aquatic species and communities by the Bay Delta Conservation Plan (BDCP). The intent of the ISA process is to ensure that the plan has access to the best available science. Our recommendations area not biding, and area not intended to either question or promote particular plan goals or policies, but are intended to help inform the planning process.
Bay Delta Conservation Plan, Non-Aquatic (2008) PDF
Bay Delta Conservation Plan, Adaptive Management
This report summarizes recommendations from a group of nine independent scientists convened in December 2008 concerning incorporation of adapative management into the Bay Delta Conservation Plan (BDCP). This report includes a general review of pertinent BDCP documents and a recommended framework for incorporating adative management into the planning, designa and implementation of the BCDP.
Bay Delta Conservation Plan, Adaptive Management (2009) PDF
Our group of advisors was assembled to offer independent review of the scientific foundations for the Eastern Merced County Natural Community Conservation Plan (NCCP)/Habitat Conservation Plan (HCP), a plan in progress. The objective of our review is to ensure the quality of the data, planning principles, analytic techniques, and interpretation of analytical results. We are charged to offer an independent evaluation of the science upon which planning decisions will be made in the proposed NCCP/HCP and to provide advice about how to improve the process with sound science. We generally will not comment on the goals or outcomes of planning. Moreover, for the purposes of this review we ignore the differences between NCCPs and HCPs and, instead, focus on scientific questions of concern to both processes. Although we avoid explicit comment on policies, it is difficult to divorce a discussion of scientific issues entirely from their policy implications.
This report summarizes recommendations from a group of independent science advisors for the Butte County Habitat Conservation Plan/Natural Community Conservation Plan (HCP/NCCP). This statutorily required scientific input is provided early in the planning process to help the plan proceed with best available science. The advisors operate independent of the entities involved in planning or implementing the HCP/NCCP.
Our recommendations are advisory only and not binding on HCP/NCCP participants. They are organized by the following major topics: (1) review of the Draft Ecological Baseline Report (SAIC 2007), (2) scope of the plan, (3) information gaps, (4) conservation design, (5) conservation analyses, and (6) adaptive management and monitoring.
This Executive Summary briefly highlights important recommendations. See the full report for additional details.
This report summarizes recommendations from a group of independent science advisors for the Santa Clara Valley Habitat Conservation Plan/Natural Community Conservation Plan (HCP/NCCP). This scientific input is provided early in the planning process to help the plan proceed with best available science. The advisors operate independent of the entities involved in planning or implementing the HCP/NCCP. Our recommendations are advisory only and not binding on HCP/NCCP participants.
Our recommendations are organized by the following major topics:(1) scope of the plan, (2) review of existing information, (3) conservation design, (4) conservation analyses, and (5) adaptive management and monitoring.