Modeling Land Use Change: What can we learn from geographers? Keith C. Clarke Professor and Chair...
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Transcript of Modeling Land Use Change: What can we learn from geographers? Keith C. Clarke Professor and Chair...
Modeling Land Use Change:What can we learn from
geographers?
Keith C. ClarkeProfessor and Chair
Department of Geography/NCGIAUniversity of California
Santa Barbara
What is land use? (cover vs. use)
What is land use change?
Land use change in action
Land use transitions are slow and cumulative
Land use mapping
Land use change modeling variables
Driver (s) (Derive e.g. Burgi & Turner Ecosystems, 2002)
State probabilities (static, dynamic)Class magnitudesSpatial autocorrelation(s)Feedbacks
Change in space
Change by class: The transition matrix
Green Orange Yellow
Green 25 (1.0) 0 (0.0) 0 (0.0)
Orange 0 (0.0) 47 (0.98) 1 (0.02)
Yellow 0 (0.0) 0 (0.0) 47 (1.0)
Change sequences
Wildland to agricultureForest to agricultureWetland to agricultureAgriculture to urbanResidential to commercialAgriculture to forest
National trends
Major problemsConsistency in land use classes over timeMisregistration (false change)Scale, generalization differencesGetting long time seriesScaling up and downUsing remotely sensed data (80%)Accuracy, timeliness and costCalibration and performance
“Classic” models: Bid rent
Johann Heinrich Von Thunen 1783-1850Alonso (1964) and Muth (1969) extensions“Highest and best use”
Computer-based modeling:False startsLee, D. B. (1973) Requiem for Large-Scale
Models, Journal of the American Institute of Planners 39, pp. 163-178
Seven deadly sins of large scale models • Hypercomprehensiveness • Grossness • Hungriness • Wrongheadedness • Complicatedness • Mechanicalness • Expensiveness
So what has changed?
Better dataIKONOS, Landsat 7Comprehensive land use mapping programs
(e.g.NLCDB)Better time series
Landsat 1972-2002CORONA
Better computers (Geocomputation, tractability)
GISMore varied (better?) models
Types of Models
Economic theoryGIS-based allocationCellular automataAgent basedIntegrated modelingLink to decision-making
USFS Model inventoryA Review and Assessment of Land-Use Change Models
Dynamics of Space, Time, and Human ChoiceC. Agarwal, G. L. Green, M. Grove, T. Evans, and C. Schweik
(2000)
Model scaleTime step and durationResolution and extentAgent and domain
Model ComplexityTemporal complexitySpatial complexityHuman decision-making complexity
Models Surveyed
1. General Ecosystem Model (GEM) (Fitz et al. 1996)
2. Patuxent Landscape Model (PLM) (Voinov et al. 1999)
3. CLUE Model (Conversion of Land Use and Its Effects) (Veldkamp and Fresco 1996a)
4. CLUE-CR (Conversion of Land Use and Its Effects – Costa Rica) (Veldkamp and Fresco 1996b)
Models (2)
5. Area base model (Hardie et al. 1997)6. Univariate spatial models (Mertens et al.
1997)7. Econometric (multinomial logit) model
(Chomitz et al. 1996)8. Spatial dynamic model (Gilruth et al. 1995)9. Spatial Markov model (Wood et al. 1997)
Models (3)10. CUF (California Urban Futures) (Landis
1995, Landis et al. 1998) [CUF II]11. LUCAS (Land Use Change Analysis System)
(Berry et al. 1996)12. Simple log weights (Wear et al. 1998)13. Logit model (Wear et al. 1999)14. Dynamic model (Swallow et al. 1997)15. NELUP (Natural Environment Research
Council [NERC]–Economic and Social Research Council [ESRC]: NERC/ESRC Land Use Programme [NELUP]) (O’Callahan 1995)
Models (4)
16. NELUP - Extension, (Oglethorpe et al. 1995)
17. FASOM (Forest and Agriculture Sector Optimization Model) (Adams et al. 1996)
18. CURBA (California Urban and Biodiversity Analysis Model) (Landis et al. 1998)
19. Cellular automata model (Clarke et al. 1998, Kirtland et al. 2000) [SLEUTH]
Model #7 Entry
Model Name/Citation Chomitz et al. 1996 Model Type Components/Econometric (multinomial logit)
model Modules Single module, with multiple equations What It Explains /Dependent Variable
Predicts land use, aggregated in three classes: Natural vegetation Semi-subsistence agriculture Commercial farming
Other Variables Strengths Soil nitrogen, Available phosphorus, Slope, Ph, Wetness, Flood
hazard, Rainfall, National land, Forest reserve, Distance to markets, based on impedance levels (relative costs of transport), Soil fertility
Model #7 Entry (ctd)
Strengths Used spatially disaggregated information to calculate an
integrated distance measure based on terrain and presence of roads
Also, strong theoretical underpinning of Von Thunen’s model
Weaknesses Strong assumptions that can be relaxed by alternate
specifications. Does not explicitly incorporate prices.
Drivers in the 19 Models Population
SizeGrowthDensity
Returns to Land-Use (costs and prices) Job Growth Costs of Conversion Rent Collective Rule Making and Zoning Tenure
Drivers (2) Relative Geographical Position to Infrastructure:
Distance from Road Distance from Town/Market Distance from Village Infrastructure/Accessibility Presence of Irrigation Generalized Access Variable
Village Size Silviculture Agriculture Technology Level Affluence Human Attitudes and Values Food Security Age
Economic models
Alonso/Muth traditionMultinomial logitDifferential equationsSteady state/equilibrium models (e.g.
demand = supply)Externally determined empirical
relationshipsCan be stochastic
Economic-based modelsAssume bid rent or other land demandDerive formulae linking variables, space
and distance, often GIS operationCompute potential for each unit of
granularity (e.g. pixels, parcels, LDUs)Allocate exogenously determined growth
amount by land usePrioritize allocation by rank or
stochastically
GIS-based allocation
Use GIS to compute land transition potential (transition matrix)
Use spatial landscape metrics to predetermine allocations
Assign specific numbers of granules new land use types based on rules
Stop when allocation demands are metOften single time incrementExample is CUF II
Cellular Automata
Gridded worldCells have finite statesRules define state transitionsTime is incrementalCells are autonomous, act as agentsSelf-replicating machines: Von NeumannClassic example is Conway’s LIFE
Urban Cellular Automata
Cells are pixelsStates are land usesNeighborhood is definedTime is “units”, e.g. yearsRules determine growth and changeDifferent models have different rule setsMany models now developed, few tested
SLEUTH CA Growth Rules
Behavior typesSpontaneousNew spreading centersOrganicRoad influence
Land use change: Deltatron modelTight coupling
Spontaneous Growth
f (diffusion coefficient, slope resistance)
urban settlements may occur anywhere on a landscape
Creation of new spreading centers
f (spontaneous growth, breed coefficient, slope resistance)
Some new urban settlements will become centers of further growth. Others will remain isolated.
Organic Growth
f (spread coefficient, slope resistance)
The most common type of development occurs at urban edges and as in-filling
Road Influenced Growth
f (breed coefficient, road_gravity coefficient, slope resistance, diffusion coefficient)
Urbanization has a tendency to follow lines of transportation
SLEUTH rule sequence
T0 T1
spontaneousspreading
center organicroad
influenced deltatron
Behavior Rules
T0 T1
For i time periods (years)
spontaneousspreading
center organicroad
influenced deltatron
f (slope resistance, diffusion
coefficient)
f (slope resistance,
breed coefficient)
f (slope resistance,
spread coefficient)
f (slope resistance, diffusion coefficient,
breed coefficient,road gravity)
Patterns/process of land cover change
Introduction of new land cover type (invasion, diffusion)
Land cover class extension from edges (spread, contagion)
Perpetuation of change (lagged autocorrelation)
Deltatron Dynamics:
To/From Transition matrix Table of land cover class average slopes Urbanization drives change within the
model Urban (and others) invariant class
Land cover Delta-space
Deltatrons at work
“Bringer of change” (semi-independent agent) Placeholder of where and what type of land cover
transition took place during its lifetime Tracks how much time has passed since a change
has occurred (Lifetime) Enforces spatial and temporal auto-correlation of
land cover transitions by its life cycle
A Deltatron is:
Deltatron Land Cover Model
Phase 1: Create change
YEL 1.20%ORN 3.30%GRN 5.60%
Averageslope
For n newurban cells
select random pixel
change land cover
spreadchange
Select two land classes at random
Of the two:Find the land class
most similar to current slope
YEL ORN GRNYEL 0.9 0.05 0.05ORN 0.05 0.9 0.05GRN 0.1 0.1 0.8
Transition ProbabilityMatrix
Check the transition
probability
Create delta space
Deltatron Land Cover ModelPhase 2: Perpetuate change
YEL ORN GRNYEL 0.9 0.05 0.05ORN 0.05 0.9 0.05GRN 0.1 0.1 0.8
Transition ProbabilityMatrix
search for change in the neighborhood find associated
land cover transitions
createdeltatrons
impose change inland cover
Age orkill
deltatrons
delta space
Prediction (the future from the present)
Probability Images
Alternate Scenarios
Land cover uncertainty
Agent based models
Agent is entity impacting change (e.g. farmer, business, household)
Agents are independent, spatially located, tracked separately, and updated
Behavior is preprogrammed, can also be reactive (e.g. to neighborhood or proximal agents)
Can have different types of agents with interactions (e.g. predator-prey)
Highly stochastic, performance hard to evaluate
(Bio) ComplexityNon-linear feedback (inter-agent
reactions)Multi-scale feedbacksBifurcations and phase changesCollapse/extinction possibleEmergenceEvolution and AlifeSWARM, STELLA, Ascape, etc.
Examples
Emilio Moran’s group (Indiana Univ)Change detection from remote sensingDemographic analysisParticipant interviews, decision-basedTest model in Midwest and AmazonAlso Dan Brown et al. at U Michigan
(SWARM)
Integrated Modeling
Multi-system modelingGeneralized modelsSupermodelsCoupled and linked models
GIS required for data handling, calibration, forecasts, etc
Coupling not so simple
GIS/EM: The integration challenge
Model integration
• Park & Wagner TGIS 1997• Isolated, Loose, Tight, Integrated
Share data from GISHave common input/output layersLink inputs to outputsHave a single user interface (UCIME)Hide the models from the userInteract via scenarios (integrate via
planning/decision-making process)
The UCIME Web Interface
Data/World Scenarios
Users/Decision MakersIndividual
Group
Convergence
Scenario as model/plan bridge
Model
Environmentalist
0
10
20
30
40
50
1 4 7 10 13 16 19 22 25
Question
Sce
nar
io D
ista
nce
Unrestrained
Follow Current
Road Growth
Growth Boundary
EnvironmentFriendly
No Commercial
Neutral Responses
0
10
20
30
40
501 4 7 10 13 16 19 22
Questions
Sce
nar
io D
ista
nce Unrestrained
Follow Current
Road Growth
Growth Boundary
Environment Friendly
No Commercial
Good scenario sets
Themes can be single or multipleHow many? 7+-2Relevance: Policy implicationComprehensive (drivers)DiverseCreative: Role for VisualizationTransparentCoherent: properly formulated and plausibleConsistent
Scenario Difference
Urban models in UCIME
Population density structureSLEUTH (Urban form and land use)SCOPEBy very loose coupling
HydrologyAir qualityWildfire hazard
ConclusionReviewed major concepts, problems in land use
change modelingCovered major contemporary types of modelsImportance of drivers and quantification of first
and second derivativesSets of models when integrated are more
powerful than when used alone, or when one metamodel is formulated
Users want credibility in modeling/ersScenarios are key to bridging models and views