DEPUTY ASSISTANT SECRETARY FOR FISH AND WILDLIFE AND PARKS DEPARTMENT OF THE INTERIOR
BEFORE THE HOUSE RESOURCES COMMITTEE
SEPTEMBER 10, 2004
Mr. Chairman and Members of the Committee, I am Julie MacDonald, Deputy Assistant Secretary for Fish and Wildlife and Parks in the Department of the Interior (Department). I am pleased to appear before you today to discuss the Endangered Species Act (ESA or Act).
We appreciate the Committee’s interest in examining the impact of the ESA on Southern California, an area of great biological and ecosystem diversity and one of the fastest growing regions in the United States. Given the large amount of federal lands in Southern California, we are acutely aware that the resource management decisions we make can profoundly impact local communities. However, we believe that resource management does not need to come at the expense of the needs of local communities, and the Administration is committed to achieving a balance between conservation and growth using all the available tools. At the Department, this commitment means implementing a cooperative approach toward the recovery of endangered and threatened species through the development of partnerships with states, tribes, landowners, and other stakeholders. To that end, I would like to discuss how the Administration is working to make implementation of the ESA more efficient and effective.
Designation of Critical Habitat
The Service has characterized the designation of critical habitat as required by the Act as the most costly and least effective class of regulatory actions undertaken by the Service. It is often of little additional value or counterproductive and can result in negative public sentiment to the species and the Act itself. This negative public sentiment is fueled by inaccuracies in the initial area designated when we must act with inadequate information to meet strict statutory deadlines. For example, under the Act, the Service is required to designate critical habitat concurrent with a final listing determination, using the best scientific data available. Unfortunately, in some circumstances, the information supporting such designations have later been found to be incomplete, sometimes resulting in a cycle of litigation, described in further detail below.
In addition, there is often a misconception among the public that, if an area is outside of the designated critical habitat, it is of no value to the species. At the same time, the designation of critical habitat imposes burdensome requirements on federal agencies and landowners and can create significant economic and social turmoil.
The accelerated schedules of court-ordered designations have left the Service with limited ability to take additional time for review of comments and information to ensure the rule has addressed all the pertinent issues before making decisions on listing and critical habitat proposals, due to the risks associated with noncompliance with judicially imposed deadlines. This in turn fosters a second round of litigation in which those who will suffer adverse impacts from these decisions challenge them. This cycle of litigation appears endless, is very expensive, and in the final analysis provides relatively little protection to listed species.
Extensive litigation has shown that the courts cannot be expected to provide either relief or an answer, because they are equally constrained by the strict language of the Act. The Department of Justice has defended these lawsuits and sought to secure relief from the courts to allow the Service to regain the ability to prioritize the listing program according to biological need. Almost universally, the courts have declined to grant that relief.
In 2001, a federal district judge, in Center for Biological Diversity v. Norton, No. CIV 01-0258 PK/RLP (ACE), observed that “the Secretary is caught in a quandary” in trying to “fulfill the myriad of mandatory [ESA] duties.” The judge opined that “[m]ore lawsuits will inevitably follow” unless, among other things, the Service regains its discretion to prioritize its workload. The judge suggested that a legislative solution is necessary; otherwise “tax dollars will be spent not on protecting species, but on fighting losing battle after losing battle in court.”
Other courts have agreed with this assessment. Simply put, the listing and critical habitat program is now operated in a “first to the courthouse” mode, with each new court order or settlement taking its place at the end of an ever-lengthening line. We are no longer operating under a rational system that allows us to prioritize resources to address the most significant biological needs. I should note that it is as a direct result of this litigation that we have had to request a critical habitat listing subcap in our appropriations request the last several fiscal years in order to protect the funding for other ESA programs. At this point, compliance with existing court orders and court-approved settlement agreements will likely require funding into fiscal year 2008.
However, additional funding to stem the tide of this “deadline” litigation is not the solution. When Congress included strict deadlines to ensure that listing measures are completed in a timely manner they could not have foreseen that litigation over deadlines would highjack the program. This highlights the need for a specific legislative solution. The Department and the Congress must work together to determine how to get the most value for species conservation out of the federal resources devoted to the endangered species listing program.
Former Secretary Bruce Babbitt wrote in a New York Times op-ed piece in April 2001 that, in its struggle to keep up with court orders, the Service has diverted its best scientists and much of its budget for the ESA away from more important tasks like evaluating candidates for listing and providing other protections for species on the brink of extinction. We also believe that available resources should be spent focusing on actions that directly benefit species such as improving the consultation process, development and implementation of recovery plans, and voluntary partnerships with states, tribes, and private landowners.
Some of the more significant and efficacious elements of a modern conservation strategy that we have pursued include candidate conservation agreements, habitat conservation plans, safe harbor agreements, voluntary agreements with landowners such as through the Service’s Partners for Fish and Wildlife Program, incentive-based actions such as those carried out under the Service’s Landowner Incentive Program, partnerships with states, tribes, and nongovernmental organizations, and private stewardship efforts by individuals and businesses. These programs, which consist of combined private and governmental action, improve the health of our lands, forests, rivers, and other ecosystems. Their implementation provides far greater conservation benefits than the designation of critical habitat while avoiding the regulatory, economic and social disadvantages of critical habitat designations.
Habitat Protection through Cooperative Conservation
We are continually working to find new and better ways to encourage voluntary conservation initiatives. Indeed, the Service currently has many conservation tools available which provide for close cooperation with private landowners, state, tribal, and local governments, and other non-federal partners that are particularly important in our implementation of the ESA. For example, through the Candidate Conservation program, the Service can work with states, landowners, and other non-federal partners to voluntarily conserve candidate or other declining species. Under this program, the Service works to identify species that face threats that make listing under the ESA a possibility and provides information, planning assistance, and resources to encourage voluntary partnerships and agreements. These resulting conservation agreements or plans may contribute to removing the threats that might otherwise necessitate listing under the ESA.
Most recently, a Candidate Conservation Agreement, developed by the Bureau of Land Management (BLM), the State of Idaho, the Idaho Army National Guard, and several private property owners who hold BLM grazing permits, served as part of the basis for the Service’s determination to withdraw its proposal to list the slickspot peppergrass (Lepidium papilliferum). Among other information central to the Service’s decision to withdraw the proposal, this formalized agreement was determined to reduce risk to the slickspot peppergrass such that this species is unlikely to become endangered within the foreseeable future. The slickspot peppergrass story is an outstanding example that listing a species and designating critical habitat is not necessarily the only means to achieve conservation.
Similar to Candidate Conservation Agreements, Safe Harbor Agreements also serve as a means to garner non-Federal property owners’ support for species conservation on their lands. Under Safe Harbor Agreements, non-Federal property owners who commit to implement voluntary conservation measures for listed species will receive assurances that no additional future regulatory restrictions will be imposed.
In addition, the Habitat Conservation Planning Program provides a flexible process for permitting the incidental take of threatened and endangered species during the course of implementing otherwise-lawful activities. The program encourages applicants to explore different methods to achieve compliance with the ESA and to choose the approach that best meets their needs. Perhaps the Program’s greatest strength is that it encourages locally developed solutions to listed species conservation, while providing certainty to permit holders. Through this process of consultation and cooperation with our partners, the Program helps provide for the conservation of listed species on non-federal land throughout the country.
On May 8, 2003, the Service announced a new conservation banking guidance to help reduce piecemeal approaches to conservation by establishing larger reserves and enhancing habitat connectivity, while saving time and money for landowners. This guidance, which has been in place since May 2003, details how, when, and where the Service will use this collaborative, incentive-based approach to species conservation.
Critical Habitat Exclusions
These are among the many conservation tools we use that play an important role in our implementation of the ESA. It is our view that where programs provide for species conservation and management, critical habitat designation is not needed. Our support for this interpretation is derived from the definition of “critical habitat” under Section 3 of the Act which states that critical habitat includes areas occupied by the species “on which are found those physical or biological features (I) essential to the conservation of the species and (II) which may require special management considerations or protection” It has been our view that areas that are not in need of special management considerations or protections are outside the definition of “critical habitat,” and are, therefore, excluded from designation.
However, a court decision in the District of Arizona has cast doubt on this interpretation. In a case involving Forest Service lands, the U.S. District Court in Arizona ruled that this interpretation is incorrect, and found that the fact that lands require special management necessitates their inclusion in, not exclusion from, critical habitat.
Although the decision is limited to the critical habitat designation at issue in that case, it may negatively affect our future ability to use this interpretation of “critical habitat” elsewhere. The Service uses other methods besides this policy to encourage voluntary and cooperative conservation. For example, Section 4(b)(2) of the ESA allows the Department to exclude areas if the benefit of exclusion outweighs that of inclusion as long as it does not result in the extinction of the species. This Administration has used this provision to exclude lands subject to Habitat Conservation Plans and other conservation agreements or management strategies designed to conserve species.
Cooperative Conservation at Work in Southern California
Deemed a “biological hotspot” by biologists and other researchers, Southern California supports a rich diversity of fish, wildlife, and plant species because of the area’s unique geological, hydrological, climatic, and topographic characteristics. As one of the most ecologically diverse areas in the country, Southern California has approximately 100 species listed as threatened or endangered under the Act. In the State of California alone, there are 292 federally listed species, 2 proposed, 16 candidate species, as of June 24, 2004.
The area is also one of the fastest growing regions in the United States. With a projected population of 19 million people, Southern California has five of the six most populous counties in the nation. Riverside County is one of California’s fastest growing counties and its population of approximately 1.1 million in 1990 is projected to increase to 1.8 million by 2005. Orange County, although already very densely populated, will likely rise from its current level of 2.9 million to just over 3 million within the next four years. San Bernardino County’s population is also on the upswing, with an anticipated increase from 1.4 million residents in 1990 to almost 2 million by 2005. Los Angeles County, already approaching the 10 million mark, is more populous than 42 of our Nation’s states.
Conserving California’s natural resources, while accommodating the projected population growth, has required the innovative use of cooperative conservation in administering the ESA. For example, in June 2004, the Service approved the Western Riverside County Multiple Species Habitat Conservation Plan(HCP). Under this landmark agreement, a proposed 500,000 acre reserve system was created as habitat for 146 species through the combined efforts of federal, state, and local partners. Through this regional HCP, the County of Riverside and local jurisdictions will be able to proceed with economic development projects, while fully complying with the mandates of the Act.
As we continue to improve upon a more holistic, ecosystem-based approach in administering the HCP program, it is our hope that the Western Riverside County Multiple Species Habitat Conservation Plan will serve as an example for future HCP’s. As previously mentioned, pursuant to our authority under Section 4(b)2 of the Act, we have excluded lands that are subject to these plans from critical habitat designation.
Such tools will become all the more important as Southern California continues to experience unprecedented growth.
In closing, I would like to reiterate our commitment to working with Congress to find a solution to the problems associated with critical habitat designation and other related issues. At the same time, the Department will continue to strengthen our partnerships and expand the use of cooperative conservation tools. It is our goal to use cooperative conservation and the tools at our disposal to implement programs that will eliminate the need for listing by conserving species before they become threatened.