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Fish 558 - Fall 2013 Decision Analysis in Natural Resource Management

Fish 558 - Fall 2013 Decision Analysis in Natural Resource Management. Basic Information. Instructor: Dr Andre Punt (FISH 116A; aepunt@u ) Office hours: Class web-site http://courses.washington.edu/fish558/ Prerequisites for this course Fish 458 (or talk to me)

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Fish 558 - Fall 2013 Decision Analysis in Natural Resource Management

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  1. Fish 558 - Fall 2013Decision Analysis in Natural Resource Management

  2. Basic Information • Instructor: • Dr Andre Punt (FISH 116A; aepunt@u) • Office hours: • Class web-site • http://courses.washington.edu/fish558/ • Prerequisites for this course • Fish 458 (or talk to me) • Knowledge of population dynamics models, with and without age structure • Experience with non-linear parameter estimation • Knowledge of probability theory and likelihood • Familiarity with R (e.g. FISH 552, 553)

  3. Class Structure • Lectures (Room 213): Mon, Wed (9.30 -11.20) • Five homework assignments (including one project) • Class evaluation: • Submission of homework assignments. • Homework assignments (15-25% each).

  4. Course Overview • How and when to use risk analysis. • Evaluating the probability of alternative hypotheses using Bayesian methods. • Evaluating the consequences of management actions.

  5. Key Note • This is a survey course intended to expose you to the topics and get you started. • A full course could easily be devoted to each of the subjects covered. • What you get out of the course will depend on how much you delve into it. • I will simply assure you can do some simple problems.

  6. Course Readings(see Web Site for Full Listing) • Burgman, M.A., Ferson, S., Akçakaya, H.R. 1994. Risk Assessment in Conservation Biology, Chapman & Hall. • Hilborn, R., Mangel, M. 1997. The Ecological Detective. Princeton.

  7. Estimation Methods (Overview) Age structure Spatial structure Lumped models Size structure Trophic interactions

  8. Estimation(Desired Outputs) • Stock size (spawning biomass, exploitable biomass). • Reference points (BMSY, B0, 0.2B0). • Age-, size-structure of the population.

  9. Estimation(Typical inputs) • Biological parameters: • Natural mortality, M. • Growth curve (length-age, weight-length). • Fecundity. • Selectivity. • Monitoring data: • Catch. • Fishery-dependent (catch-rates; catch-at-age; catch-at-length – by fleet). • Fishery-independent (survey indices; survey catch-at-age; tagging).

  10. Estimation(Basic Principles) • Specify a model of the population dynamics (age, sex, size, space, ….), i.e. the equations. • Identify the data which could be used to determine the parameters of the model: • Data to determine biological parameters (growth, fecundity, etc.) – generally used “outside” the model. • Data to determine the rest of the parameters – included in the likelihood function. • Construct a likelihood function for the second category of data. • Minimize the negative of the logarithm of the likelihood function (and evaluate fit diagnostics).

  11. Estimation(Specifying models) • All models have four components: • Basic dynamics – how do I get from this year to next year? • Recruitment / growth – how do I balance the impact of losses to natural mortality? • Catches – how do the catches impact the dynamics of the population? • Initial conditions – what was the state of the population when my model started? • Note that some of these components (e.g. catches) may be very simple for some models. However, they must all be there somewhere.

  12. Production Models –I(The basics) • Applicable when: • No information is available on the biological characteristics of the population (M, growth, etc.) • All fleets have essentially the same selectivity pattern.

  13. Production Models –II(The equations)

  14. Production Models –III(The negative log-likelihood)

  15. Production Models –IV(Advantages and disadvantages) • Advantages: • Simple, quick, nice for homework assignments! • BMSY is calculated easily. • Disadvantages: • Information on growth, catch-at-length, etc. are usually available for any species for which a reliable index of abundance is available. • Relies on the assumption that selectivity is the same for all fleets.

  16. Production Models –V(Application to Cape Hake) • Two indices of abundance (catch-rates and surveys). The likelihood function is therefore:

  17. Age-structured models(The basics) • Applicable when: • A growth curve (and its uncertainty) is available. • Some age- or size-composition data are available. • The fleets each have different selectivity patterns. • Hierarchy of age-structured models: • Backwards methods: ADAPT-VPA; tuned VPA; XSA • Forwards methods: Integrated Analysis (Synthesis, Coleriane, CASAL)

  18. Age-structured models(The equations-I) Age-structured models are as complicated as you want to make them. The following slides outline an age-structured model with two fleets, no sex-structure, and a Beverton-Holt stock-recruitment relationship

  19. Age-structured models(The equations-II) Basic dynamics

  20. Age-structured models(The equations-III) Recruitment

  21. Age-structured models(The equations-IV) Catches

  22. Age-structured models(The equations-V) Initial Conditions

  23. Age-structured models(Hints and tips on equations) • Questions arising: • Know your assumptions - Summarize the model in terms of timing (when do things happen in the model). • Start simple and extend as needed - How would you extend the model to allow for: a) sex-structure, b) time-varying selectivity, c) sex-change, d) a tagged population, and e) an MPA? • The model must produce the right outputs – Does the model produce the types of outputs we need? • Know your model parameterization – Identify the parameters of the model and how you could estimate their values?

  24. Age-structured models(The objective function-I) • The objective function is almost always case-specific (it depends on the available data). Common contributions to the objective functions include: • indices of abundance (usually log-normal, but sometimes normal / gamma); • catch-at-age (usually multinomial, but sometimes lognormal / robust normal); • catch-at-length (usually multinomial, but sometimes lognormal / robust normal); • discard data (discard rates and discard length- and age-composition information); • length-at-age (usually normal); • mean weight (usually normal); and • indices of exploitation based on tagging data (??)

  25. Age-structured models(The objective function-II) • The objective function often also includes penalties (“priors”). The most typical of these are: • a penalty on the recruitment residuals; • a penalty on the extent to which selectivity varies from one year to the next; • a penalty on the extent to which selectivity is domed-shape / monotonic; and • priors on M and steepness.

  26. Age-structured models(The objective function-III) It is necessary to compute the model-estimate of the catch- at-length when age-structured models are fitted to length- frequency data. This is usually achieved using the formula:

  27. Age-structured models(The objective function-IV) Account can be taken of age-reading error using an age-reading error matrix, viz:

  28. Age-structured models(Advantages and disadvantages) • Advantages: • Far more flexibility to include realistic population dynamic processes and data in analyses. • Disadvantages: • More complicated (mathematically and computationally) than age-lumped models. • Flexibility makes it hard to decide “when to stop”.

  29. Age-structured models(Application to Cape hake) Results of fitting a deterministic age-structured model to catch-rate and survey data for Cape hake AIC suggests that the production model fits the data best!

  30. Size-structured models(The basics) • Applicable when: • Animals cannot be aged / the growth curve is indeterminate (i.e. t0 cannot be determined). • The primary source of data is length-composition information. • Hierarchy of size-structured models: • Various “data-poor” size-based methods of stock assessment exist – most are very biased. • The size-structured models outlined here are based on the “Integrated Analysis” paradigm.

  31. Size-structured models(The equations) • Size-structured models are constructed in the same way as age-structured models, except that the basic dynamics are size- rather age-structured, i.e.:

  32. Size-structured models( expanded) Natural survival Harvest survival Growth The matrix X is often constrained to prevent “negative growth” (e.g. lobsters, abalone)

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