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Towards the analysis of ecological time series using state-space models

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(1)

Soledad CASTANO

(1,2)

, Hélène GUIS

(1)

, Jean VAILLANT

(3)

, Thomas BALENGHIEN

(1)

, Jean-Claude DELECOLLE

(4)

, Thierry BALDET

(1)

and David PLEYDELL

(1,2)

(1)French Agricultural Research Center for International Development (CIRAD), CMAEE, Baillarguet Campus, Montpellier, France (2)Agricultural Research National Institute (INRA), CMAEE, Duclos Campus, Guadeloupe, France (3)Mathematics and Computation Department, University of Antilles and Guyane, Pointe-à-Pitre, Guadeloupe (4)Strasbourg Institute for Parasitology and Tropical Diseases, Strasbourg, France

Towards the analysis of ecological time series

using state-space models

References

1 - M.R. Easterling, S.P. Ellner and P.M. Dixon. Size-specific sensitivity: Applying a new structured population model. Ecology 81, 694–708, 2000. 2 - C. Andrieu, A. Doucet, and R. Holenstein. Particle Markov chain Monte Carlo methods. J. Royal Statistical Society B, 72(2):1–33, 2010.

3 - R. Venail, T. Balenghien, H. Guis, A. Tran, et al. Assessing diversity and abundance of vector populations at a national scale: example of Culicoides surveillance in France after Bluetongue virus emergence. Arthropods as Vectors of Emerging Diseases: Springer Berlin Heidelberg. 77–102, 2012.

European Conference on Mathematical and Theoretical Biology, 15-19 Juin 2014, Gothenburg, Sweden

Introduction & Framework

Results

THE METHODOLOGICAL CHALLENGE

• Identify a model structure that can minimise prediction error. • Quantify uncertainty via Bayesian methods.

• Generate priors from laboratory data.

• Calibrate models to surveillance network time series.

• Obtain efficient Markov Chain Monte Carlo mixing for SSMs.

MATRIX POPULATION MODELS

• Between-individual heterogeneity in a physical characteristic is repressented by splitting components of matrix M in a discretised IPM approach.

• This approach accounts for heterogeneity in degree-day accummulation & represents the metabolic status of individuals.

• Kernel parameters were estimated to reproduce development time distributions of each stage at various fixed temperatures T.

MODELLING THE LIFE CYCLE OF CULICOIDES

DATA FOR KERNEL ESTIMATION

Ecological time series provide incomplete snapshots of a system. Using such data to predicting population level responses to global change is the holy grail of population dynamics.

State-space models (SSM), which couple stochastic dynamic models of the “state-space” with models accounting for imperfect observation, offer an attractive solution.

INTEGRAL PROJECTION MODELS

(1)

(IPM)

• Mathematical and computational simplicity possible.  e.g. constant scalar elements & linear dynamics • But, ignore between-individual heterogeneity in developmental response to environmental variation.

Example adult

abundance time series

 

K

y

x

n

x

t

dx

p

y

x

f

y

x

n

x

t

dx

t

y

n

(



,

1

)

(

,

)

(

,

)

(

,

)

(

,

)

(

,

)

pop. vec. at t+1 KERNEL pop. vec. at t survival-growth fertility

Midges of the genre Culicoides transmit several animal

diseases (i.e. Bluetongue, Schmallenberg, AHS).

 Modelling Culicoides’ life cycles is crucial for predicting epidemic outcomes & quantifying control efficacy.

 The French National Culicoides Surveillance Network provides a rich source for confronting models with data.

EGGS

PUPAE

t t A A P P L E A E t t Mn A P L E P T P T P T F P A P L E n                                           0 0 0 0 0 0 0 0 1 1 between-stages

transition probabilities per capita fertility

Proportion of completed development, T=20ºC

from Venail et al.(3) (2012)

Life stage Eggs, Larvae & Pupae Adults

Data source Various published studies Unpublished laboratory data

Comments Imputation of missing sample sizes required estimating p(survival) from a similar study

Provides distributions for egg

production & gonotrophic cycle length

Survival probability estimates permitted Bayesian imputation

of missing sample sizes.

Imputed sample sizes helped quantify uncertainty in kernel

parameters (mean & standard deviation).

Truncated Gaussian kernels were estimated with a fifty

developmental sub-unit resolution at fixed temperatures.

Development times were shortest at T=30°C, greatest at

T=17°C & most variable at T=17°C.

Kernel link to temperature clearly non-linear.

No. collected individuals (by catch)

No. collected individuals (monthly mean) Monthly rainfall (mm)

Monthly min temperature (ºC) Monthly max temperature (ºC)

Pupae survival was greater than egg survival at all

temperatures.

Pupae development times resembled egg development

times at most temperatures.

Variance in development times at 27°C was greater for

pupae than for eggs.

Variance in development times at 17°C was lower for pupae

than for eggs.

Perspectives

 Apply paradigm to whole life cycle.

 Explore links between kernel & environmental variation.

 Fit simple matrix models to observed time series using Particle MCMC

(2)

.

 Incorporate the IPM representation for degree-day accumulation in SSMs.

 Identify a compromise between biological detail, computation time and predictive power.

 Incorporate the full geographical extent of the surveillance data.

Références

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