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Introduction to Models Landscape Ecology

Introduction to Models

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Introduction to Models. Landscape Ecology. What are models? . What is a model?. How is it different from a theory? Hypothesis?. Theory, hypothesis, model?. Theory ( theoria – a looking at, contemplation, speculation) - PowerPoint PPT Presentation

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Page 1: Introduction to Models

Introduction to ModelsLandscape Ecology

Page 2: Introduction to Models

What are models?

Page 3: Introduction to Models

What is a model?How is it different from a theory?Hypothesis?

Page 4: Introduction to Models

Theory, hypothesis, model?Theory

(theoria – a looking at, contemplation, speculation)◦A formulation of apparent relationships or

underlying principles of certain observed phenomena which has been verified to some degree.

Hypothesis: (hypotithenai – to place under)

◦an unproved theroy, proposition, supposition◦Tentatively accepted to explain certain facts

or to provide basis for further investigation.

Page 5: Introduction to Models

Theory, hypothesis, model?Model

(modus – the way in which things are done)

◦A stylized representation or a generalized description used in analyzing or explaining something.

◦Models are tools for the evaluation of hypotheses.

Page 6: Introduction to Models

Example:Hypothesis:

◦Birds forage more efficiently in flocks than individually

Page 7: Introduction to Models

Flock Size

Cons

umpt

ion

Page 8: Introduction to Models

Example:Hypothesis:

◦Birds forage more efficiently in flocks than individually

Models:◦Consumption proportional to flock

size. ◦Consumption saturates as flock size

increases.◦Consumption increases and then

decreases with increaseing flock size.

Page 9: Introduction to Models

Questions/Comments

Page 10: Introduction to Models

Why use models?Most basic… Help test scientific

hypotheses◦Clarify verbal descriptions of nature and of

mechanisms. ◦Help define process◦No model is fully correct

So comparing models may aid in helping understand process.

◦Aid in analyzing data◦Can’t experiment◦Insights into dynamics◦Prediction

Page 11: Introduction to Models

Model as a scientific toolNeed to validate assumptionsModel needs validation

◦Compare to data? If model is inconsistent with some data…

Do we reject the model?

◦All models are wrong… The question is…

Which models are most consistent and which ones meet the challenges of new experiments and new data.

◦Comparison of multiple models.

Page 12: Introduction to Models

“The validation of a model is not that it is ‘true’ but that it generates good testable hypotheses relevant to important problems.”

Page 13: Introduction to Models

Types of modelsDeterministic

◦Same inputs… same outputs

Stochastic◦Includes probabilities

How to do this? Random number based on some distribution.

Page 14: Introduction to Models

Types of modelsScientific (Mechanistic/process

based) ◦Begins with a description of how

nature might work and proceeds from this description to a set of predictions relating the independent and dependent variables.

Statistical (empirical)◦Forgoes any attempt to explain why.◦Simply describes the relationship.

Page 15: Introduction to Models
Page 16: Introduction to Models

Develop a predictive model of how turbidity type/ intensity affects growth and survival of age-0 yellow perch

Obj 1: Develop an IBM framework

that models daily ingestion and bioenergetics

Obj 2: Integrate laboratory results to explicitly include the influence of turbidity on growth and mortality

Page 17: Introduction to Models

Individual Based Models (IBM)Uses a distribution of traits to

model natural variance in a population, not just a mean

µAttempts to recreate and predict

complex phenomena based on simple rules

Page 18: Introduction to Models

IBMs for larval/ juvenile fish and yellow perch have been developed ◦ Fulford et al. 2006, Letcher et al. 1996

Modifications of these models to explicitly include:◦ Different turbidity types and intensities ◦ Prey switching due to ontogenetic shift◦ Temporal changes in turbidity type and

intensity◦ Laboratory feeding rate data for daily

ingestion

Modification of Existing Models

Page 19: Introduction to Models

Initial Larval Condition

Page 20: Introduction to Models

Initial Larval Condition

– Initial lengths from random distribution: n=10,000 µ= 5.3 sd=0.3

– Individual weights calculated as:• Weight = 0.519*Length^3.293

Page 21: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Total Ingestion (µg/d)

Page 22: Introduction to Models

Initial Larval Condition

Ingestion Submodel

•Replaces traditional foraging submodel

•Calculated from laboratory results

• Turbidity types/ intensities and developmental stage

Total Ingestion (µg/d)

Page 23: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Daily Growth Rate (µg/d)

Bioenergetics Submodel

Total Ingestion (µg/d)

Page 24: Introduction to Models

Initial Larval Condition

• Daily Growth = (Total Ingestion*Assimilation Efficiency) - TC• -Modifiers include temperature and individual size

Ingestion Submodel

Daily Growth Rate (µg/d)

Bioenergetics Submodel

Total Ingestion (µg/d)

Page 25: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Starvation Threshold Reached?

Set to 53% of previous maximum mass

Ingestion Submodel

Daily Growth Rate (µg/d)

Bioenergetics Submodel

Total Ingestion (µg/d)

YESIndividual

DeadX

Page 26: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Starvation Threshold Reached?

Daily Growth Rate (µg/d)

Total Ingestion (µg/d)

YESIndividual

DeadX

NO

Bioenergetics Submodel

Page 27: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Starvation Threshold Reached?

Daily Growth Rate (µg/d)

Total Ingestion (µg/d)

YESIndividual

DeadX

NO

Eaten?Predation Submodel

YES

Bioenergetics Submodel

Page 28: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Starvation Threshold Reached?

Daily Growth Rate (µg/d)

Total Ingestion (µg/d)

YESIndividual Dead

XNO

Eaten?Predation Submodel

YES

NO

Update Individual’s Mass/ Length

Modified from Fulford et al 2006, Letcher et al. 1996

Next fish/ next day

Bioenergetics Submodel

Page 29: Introduction to Models

Model ConstructionEach model run starts with 10,000

individuals◦ Several runs per “condition”

Simulation of 120 days post-hatch

Switch in feeding regime at 30 mm to simulate ontogenetic shift◦ Inclusion of larger benthic prey types ◦ Larval vs. Juvenile feeding rates

Page 30: Introduction to Models

Initial Model Comparisons•“Static” conditions• No variance in intensity or type over the 120 days

•Low and High conditions for both turbidity types– Low ~ 5ntu– High ~ 100ntu

–Comparison of absolute impact of each type and intensity

Page 31: Introduction to Models

Large differences in growth between type and intensity

High algae

Low algae

High sediment Low sediment

Page 32: Introduction to Models

Types of modelsAnalytical

◦Numeric solution

Simulation◦No numeric solution, requires

computers

Page 33: Introduction to Models
Page 34: Introduction to Models

Net Logo….

Page 35: Introduction to Models

Types of modelsDynamic

◦Change through time

Static◦Constant relationships

Page 36: Introduction to Models

Spatial modelsWhen is a spatial model needed?

◦Distance or arrangement is important.

Page 37: Introduction to Models

Spatial modelsSpatial pattern is in independent

variable. ◦Examples?

Predicting spatial variation through time. ◦Examples?

Processes or biotic interactions generate pattern.◦Examples

Page 38: Introduction to Models

AssignmentLandscape ecological models…Next three lectures will cover

Neutral models and dispersal. Find two papers:

◦One with a neutral model ◦One with a model of dispersal

Describe:◦Primary question/objective◦Model type◦Data needs◦Validation

Page 39: Introduction to Models

Building a model…What does it take?

Page 40: Introduction to Models

Building a modelDefining the problem –

◦Not trivial◦Most crucial step in research.

Like to just go and observe/measure

Page 41: Introduction to Models

Building a modelConceptual Model

Page 42: Introduction to Models

b) Conceptual Model of Microcosm

Page 43: Introduction to Models

Building a modelWhat type of model?

◦What is the expected use of the model?

◦Data availability?

Page 44: Introduction to Models

Building a modelModel development

◦So many types of models….

Page 45: Introduction to Models

Building a modelComputer Implementation

◦Are there existing packages?◦Developing your own code…

Page 46: Introduction to Models

Building a modelParameter Estimation

◦Data from literature.◦Change value of parameters and see

how model output fits empirical data.

Page 47: Introduction to Models
Page 48: Introduction to Models

Random Discharge

Page 49: Introduction to Models

Weighted Discharge

Page 50: Introduction to Models

Sensitivity Local Spread Distance and p (weighted models only)10-km 20-km 30-km

Model 0.25 0.5 0.25 0.5 0.25 0.5Null 0.190   0.512   0.703Random Discharge 0.371   0.638   0.710Weighted Discharge 0.348 0.357   0.434 0.444   0.476 0.499

Specificity Local Spread Distance and p (weighted models only)10-km 20-km 30-km

Model 0.25 0.5 0.25 0.5 0.25 0.5Null 0.845   0.528   0.299Random Discharge 0.605   0.332   0.213Weighted Discharge 0.739 0.739   0.614 0.613   0.495 0.495

Kappa Local Spread Distance and p (weighted models only)10-km 20-km 30-km

Model 0.25 0.5 0.25 0.5 0.25 0.5Null 0.031   0.043   0.006Random Discharge -0.022   -0.028   -0.080Weighted Discharge 0.080 0.089   0.045 0.054   -0.028 -0.006

Page 51: Introduction to Models

Building a modelModel Evaluation

◦Does it agree with empirical data? If not… is it a bad model?

Multiple model comparisons…

Page 52: Introduction to Models

Building a modelExperimentation and Prediction

Page 53: Introduction to Models

Initial Larval Condition

Ingestion Submodel

Starvation Threshold Reached?

Daily Growth Rate (µg/d)

Total Ingestion (µg/d)

YESIndividual Dead

XNO

Eaten?Predation Submodel

YES

NO

Update Individual’s Mass/ Length

Modified from Fulford et al 2006, Letcher et al. 1996

Next fish/ next day

Bioenergetics Submodel

Page 54: Introduction to Models

Model ConstructionEach model run starts with 10,000

individuals◦ Several runs per “condition”

Simulation of 120 days post-hatch

Switch in feeding regime at 30 mm to simulate ontogenetic shift◦ Inclusion of larger benthic prey types ◦ Larval vs. Juvenile feeding rates

Page 55: Introduction to Models

Conditions and ScenariosST

ATIC

DYNA

MIC

Page 56: Introduction to Models
Page 57: Introduction to Models

TuesdayNeutral Models…Bring your models!

◦Assignment will be email today.