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What is the CRI?

The Cumulative Risk Initiative (CRI), is an ongoing effort of the Northwest Fisheries Science Center (NWFSC), that assesses salmonid population trends and the impact of various actions on those trends. This project uses the following approach. First, the group analyzes data regarding the "Four Hs" (habitat, harvest, hatcheries, and hydrosystems) to assess the impact of these factors on salmonid population growth. Concurrently, the team assesses the risk of extinction and constructs population models for each species, using current survivorships for each life-stage. These models can identify the times or stages at which changing survivorship will yield the largest impact on population growth rates. Follow-up work entails examining whether such changes in survivorship are biologically feasible and what management options will yield the best results. Finally, as conservation actions are implemented, the National Marine Fisheries Service (NMFS), in collaboration with other regional scientists, will be engaging in ecological experiments to test hypotheses about the relationships between management actions in the 4 H’s and salmon populations.

As part of their efforts to provide scientifically rigorous support for salmonid conservation and recovery planning, CRI scientists are committed to conducting consistent and transparent analyses.

What is the CRI team doing?

CRI activities include the integration of risk factors, the development of critical definitions of viable salmonid populations, and the identification of productive habitat for viable salmonid populations (see Figure 1).

Figure 1.  Diagram showing the activities of CRI:  integration, writing of viable salmonid populations manuscripts and habitat for viable salmonid populations manuscripts.  These activities will inform other NMFS efforts, i.e. recovery, jeopardy evaluations, sustainable fisheres, technological decision support system, convservation plans, other.

INTEGRATION (across H’s, across populations, across species): One main goal of the CRI effort is to organize data where they exist, and to provide an analytical framework for integrating the effects of taking actions in different portions of fish life cycles. This framework allows us to evaluate how actions in different portions of the salmon life cycle may improve survival, reduce risks, and foster recovery. The approach being used involves four facets:

  1. Data exploration
  2. Identification of key risk factors
  3. Detailed analyses and evaluation of management options
  4. Adaptive Management: Opportunities for pathbreaking science

No single decision model, but a commitment to transparency and data access: NMFS scientists do not envision producing a single decision-theoretic model that can be conveniently queried for scientific illumination. Because there will not be a single model, NMFS envisions a wide variety of scientific dialogues and diverse approaches. A public website will be created where all data, models and analyses used by NMFS will be accessible to anyone. At the same time, NMFS is working with other federal agencies to coordinate data management and provide a dynamic decision support system. This requires investment in innovative technologies so that the insights from adaptive management can go ‘on-line’.

The value of transparency and accessibility is that no interest group will be left out – anyone can examine the data and logic, evaluate the inferences, or contribute their own analyses. This mode of doing science encourages outside participation and is less likely to disenfranchise any group.

Science as a process and not a product: As in all scientific endeavors, the approach and pending results are not fixed in stone. Instead the process will evolve, as new data are uncovered and analyzed, as modelers reap new insights, and as practical experience confronts and contradicts the very best theorizing.

Key to this process is the NWFSC monthly workshop series, alternating between a "policy" focus and a "research and development" focus. These workshops provide an opportunity for NMFS to inform others about our process/results, receive vital input from scientific peers not at NMFS, and identify important linkages between science and policy. Frequently, scientists back away from drawing conclusions because of fear of being wrong; meanwhile managers seek straightforward solutions delivered in tidy packages from scientists. It is impossible to jointly satisfy the reluctant skepticism of scientists and the pragmatic desire for tidy solutions of the policy-maker. Instead there will be a relentless back-and-forth between science and policy – with scientists wanting to say "we do not know", and decision makers asking "what is the answer". What the public, government agencies and interested groups can expect from NMFS is open dialogue, free access to data and models, and frank discussion of risks.

Time schedule: The first round of CRI research efforts should come together in a form that will be applied ESU-wide near the end of 1999 or the beginning of 2000.

Public websites detailing data and analyses used by NMFS will be in operation no later than October of 1999. These websites will include information such as habitat and population data for particular regions, statistical analyses, a simple matrix model with estimated survival and reproduction by age for different stocks, and an explanation of how those demographic rates translate into potential for population recovery.

VIABLE SALMONID POPULATIONS (VSP): NWFSC scientists are identifying key principles to be followed when assessing population- and ESU-level viability. To make these principles practical, NMFS is developing "rules of thumbs" aimed at identifying measurable population attributes that can be used to assess the status of ESU’s and thereby guide formation of recovery goals. The initial document presenting these guidelines is called the Viable Salmonid Populations (or VSP) paper. The VSP guidelines range in specificity from actual ranges of numbers to qualitative admonitions about "what to worry about" when assessing viability. The discussion of "how many populations are needed" and "where the populations should be located" for ESU-level viability is especially tentative because major technical research concerning these questions is ongoing (and will be presented in a technical workshop in December). The VSP paper is thus a starting point, and not the final word on viability assessment (see Chapter 3 for a more in-depth discussion of VSP efforts).

It is important to realize that population viability assessment is a contentious and highly technical branch of population biology. NMFS seeks to avoid rigid doctrine regarding viability while at the same time making sure that cautious standards are available. Secondly, it is important to realize that when considering what makes an ESU viable, the answers are likely to identify more than one means of achieving that goal.

HABITAT for VIABLE SALMONID POPULATIONS: NWFSC scientists are investigating relationships between habitat condition and salmon production. Freshwater habitats associated with salmon life histories are being examined largely at the subwatershed and watershed scales. The initial goal is to understand the spatial distribution of salmon production in relation to habitat conditions. The scientific process generally involves linking regions of low-medium-high salmon production to habitat conditions associated with those regions, including physical habitat characteristics and land use parameters. Once these relationships are identified, production potential for habitats where no fish data are available can then be estimated. A technical workshop concerning habitat-salmonid interactions is scheduled for September 29th and 30th.

As a longer-term goal, NMFS is also examining connections between estuaries and near-shore habitats and the survival of salmonids as they make the transition to the ocean portion of their life cycle. In addition, a better understanding of how variability in ocean conditions interacts with salmonid fluctuations is a necessary ingredient for the design of monitoring programs.

How will CRI efforts interact with other NMFS efforts?

In time, scientific efforts of the CRI will interact with a number of other NMFS efforts (see Figure 1-1). CRI methods and analyses will be flexible in order to accommodate the diversity of groups and efforts needing information. Below are descriptions of how CRI work will interact with two of these efforts: recovery planning and jeopardy evaluations. The descriptions below are intended as examples of how CRI science will inform these other efforts.

Recovery Planning

CRI integration efforts and preparation of viable salmonid population and habitat manuscripts will provide a foundation for use by Technical Recovery Teams (see Chapter 4). Technical Recover Teams will be composed of members from state, tribal, and federal co-managers, academic institutions, stakeholders and scientific organizations. Each team will be responsible for populations within a specific geographic area and will be charged with developing recovery goals for listed ESUs. Teams will undertake a range of tasks, including identifying:

  • Factors for decline and limiting factors
  • Population/ESU criteria for recovery
  • Habitat criteria for recovery
  • Early actions for recovery

Teams will use the habitat and viable salmonid populations documents as an organizing framework for establishing recovery goals. CRI researchers and other NMFS staff will work with teams to provide data and analyses germane to the recovery planning process.

Jeopardy Evaluations

ESA decision-making is not restricted to recovery planning. Habitat conservation plans, Section 7 consultations and formal jeopardy determinations are all important aspects of endangered species management; all are aspects that will be served by CRI analytical tools. For instance, the degree to which an action "jeopardizes" a species can be evaluated using the matrix models under development by the CRI. These matrix models summarize salmonid population dynamics and can be easily adapted to varying life histories. With these models, examining how a proposed action alters parameters in the projection matrices can assess the degree to which an action ‘jeopardizes’ a species.

NMFS has initially been tailoring its CRI efforts to recovery planning because many of the decisions concerning recovery planning often require only relative comparisons. In contrast, jeopardy decisions ideally require absolute assessments of survival probabilities, and such absolute assessments are much harder to make than are relative comparisons. As the tools being created for CRI are further developed, they will become increasingly useful in the panoply of endangered species decision-making that ranges from statewide habitat conservation plans to jeopardy determinations.




last modified 02/13/2007
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