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Uncertainty

Introduction to Structured Decision Making



Module 14 — Uncertainty

Outline

 What is uncertainty? Why is it important?

 Classifying uncertainty

 Estimating uncertainty

 Evaluating uncertainty

• Sensitivity analysis





What is Uncertainty?

 Our inability to precisely express some elements of the decision analysis

 This could be uncertainty in the objectives

• An inability to value the outcomes

 Or uncertainty in the predictions

• Because something is not known perfectly (how many Mus musculus are

currently in this building?)

• Or is unknown (will a Category 5 hurricane hit the US this year?)

 Reducible vs. irreducible uncertainty

• Some uncertainties can be resolved if we collect enough data

• Others cannot be resolved until after an event occurs





Why does Uncertainty Matter?

 Uncertainty might affect the decision we make

• That is, we might choose a different alternative depending on the

predictions or the valuation of the outcomes

 A good decision does not guarantee a favorable outcome, but it accounts for

uncertainty so as to provide the best chance of a favorable outcome









2011 CSP3171, Module 14 – 1 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



A Good Decision?

Favorable Outcome

Chance

Events

Unfavorable Outcome

Good Decision



Decision



Poor Decision

Favorable Outcome

Chance

Events

Unfavorable Outcome







Types of Uncertainty

 Linguistic

 Epistemic

 Aleatory





Linguistic Uncertainty

 Vagueness

• Language permits borderline cases

 Context dependence

• Meaning depends on context

 Ambiguity

• Words can have more than one meaning

 Underspecificity

• Unwanted generality in statements

 Indeterminacy of terms

• Understanding of terms changes over time

(From: Regan et al. 2002. A taxonomy and treatment of uncertainty

for ecology and conservation biology. Ecol Appl 12:618-628.)









2011 CSP3171, Module 14 – 2 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Epistemic Uncertainty

 Reducible

 Sources

• Measurement error

• Systematic error (bias)

• Model uncertainty

• Parametric uncertainty

• Structural uncertainty

• Subjective judgment





Aleatory Uncertainty

 Practically irreducible

 Environmental stochasticity

• Natural variation in systems over space and time that is difficult to predict

 Demographic stochasticity

• The chance events that happen to individuals





Exercise: Classify the Uncertainty

As specifically as possible, identify the type of uncertainty represented by the following

examples:



 Counts of bats exiting caves, used as population estimates, don’t include bats

that depart from smaller, alternate exits

____________________________________________________

 An entomologist uses the phrase “highly fecund” when talking to a mammalogist

____________________________________________________

 The size of tree rings varies from year to year

____________________________________________________

 Botanist A and Botanist B disagree on the likelihood of extinction of Blowout

Penstemon

____________________________________________________

 A study of fox survival reports the standard error of estimates

____________________________________________________

 A paper reports reproductive success in bobolinks but does not report separately

on egg, nestling, and fledgling stages

____________________________________________________

 Two models of population dynamics in introduced whooping cranes differ on

whether an Allee effect exists

____________________________________________________





2011 CSP3171, Module 14 – 3 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Epistemic Uncertainty

 Uncertainty that arises from our incomplete knowledge about our system

• This is, theoretically, reducible

 Focus on 2 forms (both contained within model uncertainty)

• Parametric uncertainty

• Structural uncertainty





Parametric Uncertainty

 Genesis

• Sampling

• Subjective judgment (if using experts)

 Expressed as

• Probability distributions for parameters

 Special issues

• Bias







Parametric Uncertainty

3

Model R2 K (est.)

Linear (MLE) 51% 11.3

Recruitment









95% CE 34% 9.6

2

95% CE 34% 17.2





1









0

0 5 10 15

Density









2011 CSP3171, Module 14 – 4 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making







BLVU rmax (and its uncertainty)

600

Convolution (iid) of:

 ~ unid (4,6)

median 10.6%

 ~ unid (20,30)

500 p ~ uni (.84, .99)

b ~ uni (.645, .79)

s0 ~ uni (.7, .9)

s1 ~ logit-norm (.76, .92)

400

Frequency









60% CI

(6.9, 14.3)

300







200







100 95% CI

(2.1, 19.2)



0

–5 % 0 5% 10 % 15 % 20 %

rmax







[Optional instructor-designed example]









2011 CSP3171, Module 14 – 5 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Structural Uncertainty

 Genesis

• Alternative ecological hypotheses

• Different stakeholder preferences

• Different intuitive experience

Subjective judgment may be involved here as well)

 Expressed as

• Alternative models

 Special issues

• Weights associated with alternative models









Florida Whooping Cranes

Model CR WH CR = Captive-Reared

Surv. Prod. Surv. Prod. WH = Wild-Hatched

1 (Worst Case) CR CR CR CR AWB = Aransas-Wood Buffalo

2 (Best Case) CR CR AWB AWB

3 (Allee) BT CR CR AWB AWB









2011 CSP3171, Module 14 – 6 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making





[Optional instructor-designed example]









2011 CSP3171, Module 14 – 7 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Estimating Uncertainty



Estimating Probabilities

 Empirical methods

• Repeated direct observation of the event in question

• Decomposition of the event into component events (e.g., event trees), with

data to inform the component events

• Modeling, with propagation of uncertainty (e.g., PVA)





Event Tree: Successful Burn

Yes Yes Yes

Fire Fire

takes hot

Crew

avail- Burn!

Yes No

able No No

Yes

Rx met

in burn No Yes Yes

window Crew Fire Fire

Yes avail- takes hot

able

No

Rx met No No

No

No again?

No



No









Estimating Probabilities

 Subjective methods (see Module 13)

• Direct elicitation from experts

• Methods for discrete and continuous distributions







Estimating Parametric Uncertainty

 Likelihood profile

 Bayesian posterior distribution

 Subjective elicitation







2011 CSP3171, Module 14 – 8 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making







Incubator Performance



After 2008 data

Probability Density









After 2007 data









-1.0 -0.5 0.0 0.5 1.0

Difference (Petersime - Kuhl)









[Optional instructor-designed example]









2011 CSP3171, Module 14 – 9 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Estimating Structural Uncertainty

 Ecological theory

• Is the genesis for the different structures

 Statistical techniques

• Can be used to estimate parameters of different models

 Model selection techniques

• Can then be used to provide initial weights for the models





Pintail Winter Survival

1.0







Additive model

Winter Survival Rate









0.9 Average point

(P-bar,s-bar)







0.8







Compensatory model



0.7







0 5 10 15

Post-harvest Population Size (millions)



[Optional instructor-designed example]









2011 CSP3171, Module 14 – 10 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Evaluating Uncertainty



Sensitivity Analysis

 Examine how the optimal decision and the expected performance are affected by

• Assumptions

• Structural & parametric uncertainty

• Probabilities

• Magnitude of uncertainty

• Weights on objectives

• Utility

• The problem framing itself

 Ask whether the decision is robust to uncertainty

• If not, consider revising aspects of the problem





Emphasis

 Examine how

• the optimal decision and

• the expected performance

 are affected by…



 That is, would your decision change?





Sensitivity Analysis Methods

 Bracketing over range of uncertainty

• e.g., tornado diagrams

 Gradient methods (derivatives)

• e.g., sensitivity & elasticity in matrix models

 Simulation

 Scenario exploration









2011 CSP3171, Module 14 – 11 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making







Do the Differences Matter?









Tornado Diagram for BLVU

1st-yr survival





Adult survival





Age at first breeding





Juvenile survival





Fecundity





Breeding propensity





Age of senescence



4% 6% 8% 10% 12% 14% 16%

Growth Rate









2011 CSP3171, Module 14 – 12 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



[Optional instructor-designed example]









Decision Tree

70,000

Fry

Yes p = 0.8

Does

it

work? No p = 0.2

EV = 58K 10,000

Fry

Yes



Add new technology

to a hatchery? Spreadsheet

No



EV = 40K 40,000

Fry









2011 CSP3171, Module 14 – 13 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making



Spreadsheet

Values Expected Values Decision

Yes &

p(tech. Yes & doesn't Don't

Scenario works) works work No Adopt Adopt



Baseline 0.8 70000 10000 40000 58000 40000 Adopt



Don't

Prob 1 0.2 70000 10000 40000 22000 40000 Adopt

Don't

Prob 2 0.4 70000 10000 40000 34000 40000 Adopt

Prob 3 0.6 70000 10000 40000 46000 40000 Adopt

Prob 4 0.8 70000 10000 40000 58000 40000 Adopt

Prob 5 1 70000 10000 40000 70000 40000 Adopt

Don't

Prob 6 70000 10000 40000 10000 40000 Adopt



Don't

High Value 1 0.8 40000 10000 40000 34000 40000 Adopt

Don't

High Value 2 0.8 45000 10000 40000 38000 40000 Adopt

High Value 3 0.8 50000 10000 40000 42000 40000 Adopt

High Value 4 0.8 55000 10000 40000 46000 40000 Adopt

High Value 5 0.8 60000 10000 40000 50000 40000 Adopt



Low Value 1 0.8 70000 0 40000 56000 40000 Adopt

Low Value 2 0.8 70000 5000 40000 57000 40000 Adopt

Low Value 3 0.8 70000 10000 40000 58000 40000 Adopt

Low Value 4 0.8 70000 15000 40000 59000 40000 Adopt

Low Value 5 0.8 70000 20000 40000 60000 40000 Adopt



Current Value 1 0.8 70000 10000 45000 58000 45000 Adopt

Current Value 2 0.8 70000 10000 50000 58000 50000 Adopt

Current Value 3 0.8 70000 10000 55000 58000 55000 Adopt

Don't

Current Value 4 0.8 70000 10000 60000 58000 60000 Adopt

Don't

Current Value 5 0.8 70000 10000 70000 58000 70000 Adopt









2011 CSP3171, Module 14 – 14 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making







SMART Spreadsheet



Alternatives

Normalized & Weighted

Consequence Matrix

Scores

Status Minor Major Status Minor Major

Objectives Goal Units

Quo Rep Rep

Wt

Quo Rep Rep

Cost Min $M 2 2 13 .25 .25 .25 0

Environ Benefits Max 0 - 10 1 3 10 .50 0 .11 .5

Disturbance Min 0 - 10 0 1 7 .25 .25 .21 0



Final

0.5 0.58 0.5

Score:



Normalized score = (sij – min(sj)) / (max(sj) – min(sj))



Spreadsheet

Spreadsheet









Class Exercise

Using the rabbit example (Rabbit v2011.xls) with the Allee effect model, explore the

sensitivity of the long-term population size, N(21), to uncertainty in the initial population

size (cell C2, range 800-3000), adult survival (cell C3, range 0.65-0.72), and juvenile

survival (cell C4, range 0.1-0.2). Note that each change of parameters may require

recalculation of the optimal strategy. Where would you invest monitoring effort?









2011 CSP3171, Module 14 – 15 USGS & USFWS-NCTC

Uncertainty

Introduction to Structured Decision Making









Summary

 Uncertainty is one of the most challenging impediments to decision-making

 An informed approach requires

• Identification of uncertainty

• Estimation of uncertainty

• Evaluation of uncertainty

• Strategies for decisions in the face of uncertainty…





Module developed by:

Sarah J. Converse, USGS Patuxent Wildlife Research Center

Michael C. Runge, USGS Patuxent Wildlife Research Center

James E. Lyons, USFWS Division of Migratory Bird Management









2011 CSP3171, Module 14 – 16 USGS & USFWS-NCTC



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