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Some theoretical aspects of source and parameter estimation in - - PowerPoint PPT Presentation

Some theoretical aspects of source and parameter estimation in atmospheric transport and chemistry Marc Bocquet (bocquet@cerea.enpc.fr) Victor Winiarek, Mohammad Reza Koohkan, Lin Wu . . . CEREA, Ecole des Ponts ParisTech and EDF R&D


slide-1
SLIDE 1

Some theoretical aspects

  • f source and parameter estimation

in atmospheric transport and chemistry

Marc Bocquet

(bocquet@cerea.enpc.fr) Victor Winiarek, Mohammad Reza Koohkan, Lin Wu . . .

CEREA, ´ Ecole des Ponts ParisTech and EDF R&D Universit´ e Paris-Est and INRIA

Observer & comprendre

INSU

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 1 / 29

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SLIDE 2

A few key theoretical elements

Outline

1

A few key theoretical elements

2

First example: Fukushima-Daiichi

3

Second example: estimation of representativeness errors

4

Future plans

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 2 / 29

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SLIDE 3

A few key theoretical elements

Context: Atmospheric constituent versus meteorology

◮ Numerical weather forecast: ◮ The global models are weakly non-linear but chaotic. ◮ They do not depend on many parameter forcing fields (radiation, friction). ◮ Quite accurate at global scale. ◮ An inverse modelling problem on the initial condition (short windows). ◮ [Offline] chemical and transport forecast: ◮ They are potentially strongly nonlinear but non-chaotic. ◮ They depend on several parameter forcing fields (emissions, boundary conditions) and many uncertain parameters (kinetic rates, species microphysical parameters, transport subgrid parametrisation, etc.). ◮ Quite uncertain. ◮ An inverse modelling problem on the initial condition and many forcing fields.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 3 / 29

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SLIDE 4

A few key theoretical elements

Context: Atmospheric constituent versus meteorology

◮ Atmospheric constituent data assimilation is more of an inverse modelling game because: ◮ we may be interested in the forcing/parameters themselves, ◮ and successful forecasts rely on an accurate estimation of the forcings. ◮ Most of the current data assimilation schemes can be applied to either subjects (OI, 3D-Var, EnKF, 4D-Var). However, my vote goes to the smoothers (4D-Var, ensemble Kalman smoothers with weakly nonlinear physics/chemistry, iterative ensemble Kalman smoothers, 4D-En-Var, etc.) ◮ The background statistics are more uncertain and difficult to build in atmospheric constituent data assimilation.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 4 / 29

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SLIDE 5

A few key theoretical elements

Successful data assimilation: It’s all about controlling the errors

◮ Problems in atmospheric constituent data assimilation: ◮ Our observations are noisy ◮ Our models are wrong (biased at the very least) ◮ Even when they are fine, observations and models do not tell the same story! i.e. representativeness errors are especially strong in this field. ◮ So successful data assimilation and especially inverse modelling is all about errors! ◮ Need to account for / estimate those errors in order to properly estimate control parameters.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 5 / 29

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SLIDE 6

A few key theoretical elements

Mathematical tools to correct/estimate the errors

◮ Statistical methods for hyperparameter estimation (parameters of R and B): ◮ Maximum likelihood [Dee, 1995], [Desroziers and Ivanov, 2001], ◮ χ2 [Tarantola, 1987], [M´

enard et al., 2000] ,

◮ L-curve [Hansen, 1992], [Bocquet and Davoine, 2007], ◮ statistical diagnostics: [Desroziers et al., 2005], [Schwinger and Elbern, 2010], ◮ (generalised) cross-validation [Whaba, 1990], ◮ online variational estimation [Doicu et al, 2010] For CO2 fluxes estimation, discussed in: [Michalak et al., 2005], [Wu et al, 2013] ◮ Estimating the parameters of model error parametrisations: a powerful paradigm when affordable [Bocquet, 2012], [Koohkan and Bocquet, 2012] ◮ Context: A deterministic model full of uncertain parameters ◮ Jointly estimate the state variables as well as the uncertain parameters. ◮ Overfit is possible. Still might lead to a powerful forecasting tool.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 6 / 29

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SLIDE 7

First example: Fukushima-Daiichi

Outline

1

A few key theoretical elements

2

First example: Fukushima-Daiichi

3

Second example: estimation of representativeness errors

4

Future plans

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 7 / 29

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SLIDE 8

First example: Fukushima-Daiichi

The Fukushima Daiichi accident

◮ Chronology: March 12: R 1 venting + explosion; March 13-14: R 3 venting + explosion; March 15: R 2 venting + explosion; March 20-22: R 2 R 3 spraying - smokes. − → Source term of major interest for risk/health agencies, NPP operators

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 8 / 29

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SLIDE 9

First example: Fukushima-Daiichi

Observations of the Fukushima atmospheric dispersion

◮ Available data: ◮ Very few observations of activity concentrations in the air: A few hundreds of

  • bservations over Japan publicly released.

◮ Several thousands of observations from the (far away) CTBO IMS network. ◮ Activity deposition: a few hundreds, but more difficult to exploit (mainly 137Cs). ◮ Hundreds of thousands of gamma dose measurements available.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 9 / 29

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SLIDE 10

First example: Fukushima-Daiichi

Reconstruction of the Fukushima Daiichi source term

◮ Using three (d = 3) heterogeneous datasets: ◮ Activity concentrations in the air, ◮ Daily measurements of fallout, ◮ Total cumulated deposits: densely distributed in space but no information in time. ◮ Yet, too few observations so that the inversion highly depends on the background. ◮ Retrieval of the cesium-137 source term σ = (σ1,σ2,...,σ504) (∆t = 1h) using J = 1 2 (µ −Hσ)T R−1 (µ −Hσ)+ 1 2σTB−1σ , σ ≥ 0 (1) where Ri = r2

i Idi is the submatrix of R related to data set i, B = m2IN.

H: Jacobian matrix of the atmospheric transport model. ◮ Nd +1 hyper-parameters to estimate simultaneously. ◮ Estimation method: maximisation of the non-Gaussian likelihood.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 10 / 29

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SLIDE 11

First example: Fukushima-Daiichi

Non-Gaussian maximum likelihood principle

◮ Non-Gaussian maximum likelihood: p(µ|r1,...,rNd ,m) = e− 1

2 µT(HBHT+R) −1µ

  • (2π)d|HBHT +R|

×

  • σ≥0

e− 1

2 (σ−σ BLUE)TP−1 BLUE(σ−σBLUE)

  • (π/2)N|PBLUE|

dσ , (2) with: σBLUE = BHT HBHT +R −1 µ , (3) PBLUE = B−BHT HBHT +R −1 HB. (4) ◮ Integral solved by Geweke-Hajivassiliou-Keane simulator (fine with several thousand variables).

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 11 / 29

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SLIDE 12

First example: Fukushima-Daiichi

Inversion results (caesium-137)

03/11 03/13 03/15 03/17 03/19 03/21 03/23 03/25 03/27 03/29 03/31 Date (UTC) 10 10 10 10 Source rate (Bq/s)

9 10 11 12

Total reconstructed activity: 13 PBq

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 12 / 29

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SLIDE 13

First example: Fukushima-Daiichi

Deposition map reanalysis

(a)

37.5

N

140

E

(b)

140

E

10 30 60 100 300 600 1000 3000

Deposition measurements map (June 2011) - Reanalysis using three datasets

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 13 / 29

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SLIDE 14

Second example: estimation of representativeness errors

Outline

1

A few key theoretical elements

2

First example: Fukushima-Daiichi

3

Second example: estimation of representativeness errors

4

Future plans

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 14 / 29

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SLIDE 15

Second example: estimation of representativeness errors

Inverse modelling of carbon monoxide fluxes at regional scale

✁4 ✁2

2 4 6 8 42 44 46 48 50 52

Traffic urban industrial suburban

◮ Using the French 600-stations BDQA network: hourly measure- ments of CO concentrations at about 80 stations. ◮ Observations highly impacted by representativeness errors (traf- fic, urban stations). ◮ Great number of observations (about 105 assimilated here, 5×105 used for validation). ◮ Control space: fluxes and volume sources parameterised with about 70×10

3 variables

at 0.25◦ ×0.25◦ resolution. − → Even in this linear physics context, 4D-Var is a method of choice.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 15 / 29

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SLIDE 16

Second example: estimation of representativeness errors

4D-Var

◮ Gradient obtained from adjoint approximated by the discretisation of the continuous adjoint model [Davoine & Bocquet, 2007; Bocquet, 2012]. ◮ Background: EMEP inventory over Europe with an uncertainty of about 100%. ◮ Cost function: J (α) = 1 2

Nα−1

h=0

(αh −1)T B−1

αh (αh −1)

+1 2

N

k=0

(yk −Hkck)T R−1

k (yk −Hkck)

+

N

k=1

φ T

k (ck −Mkck−1 −∆tek)

(5) ◮ α: control vector of scaling parameters that multiply the first guess. ◮ Observation (representativeness) errors iteratively re-scaled by χ

2 diagnosis.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 16 / 29

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SLIDE 17

Second example: estimation of representativeness errors

Results of (traditional) 4D-Var

C O RMSE C.Pear. FA2 FA5 Simulation (01/01–02/26 2005) 303 662 701 0.16 0.52 0.90 Forecast (02/26–03/26 2005) 267 642 648 0.13 0.47 0.88 Optimisation of α 396 662 633 0.36 0.59 0.92 Forecast with optimal α 343 642 589 0.33 0.53 0.90

50 100 150 200 Time (hour) 500 1000 1500 2000 Concentration (

g/m

3 )

(a) Marignane 50 100 150 200 Time (hour) 200 400 600 800 1000 1200 1400 1600 Concentration (

g/m

3 )

(b) Douai

◮ Tremendous impact of representativeness errors!

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 17 / 29

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SLIDE 18

Second example: estimation of representativeness errors

Coupling 4D-Var with a simple statistical subgrid model

A B

◮ We would like to take into account the impact of nearby sources that generate peaks

  • n the CO concentration recordings:

εrep ≃ ξ ·Πe − → y = Hc+ξ ·Πe+ ε . (6) ξ: set of statistical coefficients (influence factors).

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 18 / 29

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SLIDE 19

Second example: estimation of representativeness errors

Coupling 4D-Var with a simple statistical subgrid model

◮ Cost function of 4D-Var-ξ: J (α,ξ) = 1 2

Nα−1

h=0

(αh −1)T B−1

αh (αh −1)

+1 2

N

k=0

(yk −Hkck −ξ ·Πek)T R−1

k (yk −Hkck −ξ ·Πek)

+

N

k=1

φT

k (ck −Mkck−1 −∆tek) .

(7) ◮ R is residual error covariance matrix (smaller than R). R = E

  • εεT

= ξ ·ΠE

  • eeT

ΠT ·ξ T + R. (8)

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 19 / 29

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SLIDE 20

Second example: estimation of representativeness errors

Results of 4D-Var-ξ: Profiles (1/4)

50 100 150 200 250 300 Time (hour) 500 1000 1500 2000 Concentration (

g/m

3 )

(a) Lille Pasteur

ξi = 0.6 h.

50 100 150 200 250 300 Time (hour) 500 1000 1500 2000 2500 3000 3500 4000 4500 Concentration (

g/m

3 )

(b) Paris Boulevard p

✝riph ✝rique Auteuil

ξi = 2.7 h.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 20 / 29

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SLIDE 21

Second example: estimation of representativeness errors

Results of 4D-Var-ξ: Profiles (2/4)

50 100 150 200 250 300 Time (hour) 500 1000 1500 2000 2500 3000 Concentration (

g/m

3 )

(c) Orl✟ans Gambetta

ξi = 11.9 h.

50 100 150 200 250 300 Time (hour) 1000 2000 3000 4000 5000 6000 7000 Concentration (

g/m

3 )

(d) Nice Pellos

ξi = 45.8 h.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 21 / 29

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SLIDE 22

Second example: estimation of representativeness errors

Results of 4D-Var-ξ: Scores (3/4)

◮ Skills: C O RMSE C.Pear. FA2 FA5 Simulation (01/01–02/26 2005) 303 662 701 0.16 0.52 0.90 Forecast (02/26–03/26 2005) 267 642 648 0.13 0.47 0.88 Optimisation of α 396 662 633 0.36 0.59 0.92 Forecast with optimal α 343 642 589 0.33 0.53 0.90 Optimisation of ξ 615 662 503 0.57 0.73 0.96 Forecast with optimal ξ 574 642 451 0.56 0.76 0.97 Coupled optimisation of ξ, α 671 662 418 0.73 0.79 0.97 Forecast with optimal ξ, α 631 642 340 0.68 0.81 0.98 ◮ We found an increase of 9% in the French CO total emission. Consistent with satellite retrieval for Western Europe.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 22 / 29

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SLIDE 23

Second example: estimation of representativeness errors

Results of 4D-Var-ξ: Forecast (4/4)

◮ Validation of a 10-month forecast after the 8-week assimilation window (2005)

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec 100 200 300 400 500 600 700 800 900 1000

4D-Var analysis

  • ptimal ξ analysis

4D-Var-ξ analysis

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Date (month) 100 200 300 400 500 600 700 800 900 1000 RMSE (µ g/m

3 ) forecast forecast initialized with 4D-var forecast initialized with optimal ξ forecast initialized with 4D-Var-ξ 4D-Var analysis

  • ptimal ξ analysis

4D-Var-ξ analysis

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Date (month) 0.2 0.4 0.6 0.8 1.0 Correlation coefficient

forecast forecast initialized with 4D-Var forecast initialized with optimal ξ forecast initialized with 4D-Var-ξ

◮ Skills almost as good in the forecast period as in the assimilation time window! ◮ Seasonal effects impacting scores.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 23 / 29

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SLIDE 24

Future plans

Outline

1

A few key theoretical elements

2

First example: Fukushima-Daiichi

3

Second example: estimation of representativeness errors

4

Future plans

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 24 / 29

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SLIDE 25

Future plans

Future plans

◮ Development of an EnVar method, the iterative ensemble Kalman smoother (IEnKS,

[Bocquet and Sakov, 2013]) that

◮ + performs a variational analysis over a time data assimilation window ◮ + has flow-dependent error estimation ◮ + does not use an explicit tangent linear/adjoint ◮ - - requires localisation (no free lunch) ◮ +/- weak-constraint formalism under development ◮ Solves the Bayesian problem with minimal Gaussian assumptions (has the potential to

  • utperform 4D-Var and EnKF in all regimes)

◮ Potentially well suited for joint state and parameter estimation, with nonlinear dependencies.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 25 / 29

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SLIDE 26

Future plans

Future plans

◮ The augmented state formalism is convenient for the IEnKS, and offers an easy implementation of technically challenging data assimilation problems. ◮ Lorenz ’95 with joint estimation of the forcing parameter F (41 variables): RMSEs. Method / F profile Sinusoidal Step-wise EnKF 0.063 0.079 EnKS L=50 0.040 0.063 4D-Var L=50 0.030 0.045 MDA IEnKS L=50 0.020 0.031

1000 2000 3000

Time

7,4 7,6 7,8 8 8,2 8,4 8,6 8,8

Retrospective analysis of parameter F

EnKF-N EnKS-N L=50 4D-Var L=50 MDA IEnKS-N L=50 Truth

1000 2000 3000

Time

7,5 8 8,5 9

Retrospective analysis of parameter F

EnKF-N L=50 EnKS-N L=50 4D-Var L=50 MDA IEnKS-N L=50 Truth

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 26 / 29

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SLIDE 27

Future plans

Future plans

◮ Development of low-order models that couple a Lorenz model and a chemical model.

100 200 300 400 500 600 5 10 15 20 25 30 35

  • 7.5
  • 5.0
  • 2.5

0.0 2.5 5.0 7.5 10.0 12.5

100 200 300 400 500 600 5 10 15 20 25 30 35

5.0 10.0 15.0 20.0 25.0 30.0 35.0 40.0 45.0

Lorenz ’95 coupled to a tracer model. ◮ The goals of this study will be: ◮ to probe the added value of online/coupled models DA vs offline models DA, ◮ to probe the added value of joint state and parameter estimation, integrated data assimilation, ◮ to assess the nonlinearity and the numerical cost of these games.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 27 / 29

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SLIDE 28

Future plans

References I

◮ Bocquet, M., 2012a. An introduction to inverse modelling and parameter estimation for atmospheric and

  • ceanic sciences. In: Blayo, E., Bocquet, M., Cosme, E. (Eds.), Advanced data assimilation for
  • geosciences. Oxford University Press, Les Houches school of physics.

◮ Bocquet, M., 2012b. Parameter field estimation for atmospheric dispersion: Application to the Chernobyl accident using 4D-Var. Q. J. Roy. Meteor. Soc. 138, 664–681. ◮ Bocquet, M., Sakov, P., 2013. Joint state and parameter estimation with an iterative ensemble Kalman

  • smoother. Nonlin. Processes Geophys. 0, 0–0, in press.

◮ Davoine, X., Bocquet, M., 2007. Inverse modelling-based reconstruction of the Chernobyl source term available for long-range transport. Atmos. Chem. Phys. 7, 1549–1564. ◮ Dee, D. P., 1995. On-line estimation of error covariance parameters for atmospheric data assimilation.

  • Mon. Wea. Rev. 123, 1128–1145.

◮ Desroziers, G., Berre, L., Chapnik, B., Poli, P., 2005. Diagnosis of observation, background and analysis-error statistics in observation space. Q. J. Roy. Meteor. Soc. 131, 3385–3396. ◮ Desroziers, G., Ivanov, S., 2001. Diagnosis and adaptive tuning of observation-error parameters in a variational assimilation. Q. J. Roy. Meteor. Soc. 127, 1433–1452. ◮ Doicu, A., Trautmann, T., Schreier, F., 2010. Numerical Regularization for Atmospheric Inverse Problems. Springer and Praxis publishing. ◮ Elbern, H., Strunk, A., Schmidt, H., Talagrand, O., 2007. Emission rate and chemical state estimation by 4-dimensional variational inversion. Atmos. Chem. Phys. 7, 3749–3769.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 28 / 29

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SLIDE 29

Future plans

References II

◮ Hansen, P. C., 1992. Analysis of discrete ill-posed problems by means of the L-curve. SIAM Review 34, 561–580. ◮ Koohkan, M. R., Bocquet, M., 2012. Accounting for representativeness errors in the inversion of atmospheric constituent emissions: Application to the retrieval of regional carbon monoxide fluxes. Tellus B 64, 19047. ◮ Saunier, O., Mathieu, A., Didier, D., Tombette, M., Qu´ elo, D., Winiarek, V., Bocquet, M., 2013. An inverse modeling method to assess the source term of the Fukushima nuclear power plant accident using gamma dose rate observations. Atmos. Chem. Phys. 0, 0–0, in press. ◮ Tarantola, A., 1987. Inverse Problem Theory. Elsevier. ◮ Vogel, C. R., 2002. Computational Methods for Inverse Problems. SIAM, Frontiers in Applied Mathematics. ◮ Wahba, G., 1990. Spline Models for Observational Data. CBMS-NSF Regional Conference Series in Applied Mathematics 59. SIAM, Philadelphia. ◮ Winiarek, V., Bocquet, M., Duhanyan, N., Roustan, Y., Saunier, O., Mathieu, A., 2013. Estimation of the caesium-137 source term from the Fukushima Daiichi nuclear power plant using a consistent joint assimilation of air concentration and deposition observations. Atmos. Env. 0, 0–0, in press. ◮ Winiarek, V., Bocquet, M., Saunier, O., Mathieu, A., 2012. Estimation of errors in the inverse modeling

  • f accidental release of atmospheric pollutant: Application to the reconstruction of the cesium-137 and

iodine-131 source terms from the Fukushima Daiichi power plant. J. Geophys. Res. 117, D05122.

  • M. Bocquet

ECMWF workshop, 22-24 October 2013, Reading, UK 29 / 29