<?xml version="1.0" encoding="utf-8"?>
<raweb xmlns:xlink="http://www.w3.org/1999/xlink" xml:lang="en" year="2013">
  <identification id="clime" isproject="true">
    <shortname>CLIME</shortname>
    <projectName>Coupling environmental data and simulation models for software integration</projectName>
    <theme-de-recherche>Earth, Environmental and Energy Sciences</theme-de-recherche>
    <domaine-de-recherche>Digital Health, Biology and Earth</domaine-de-recherche>
    <urlTeam>http://www-rocq.inria.fr/clime/index.en.html</urlTeam>
    <datecreation>2005 September 01</datecreation>
    <structure_exterieure type="Labs">
      <libelle>Centre d'Enseignement et de Recherche en Environnement Atmosphérique</libelle>
    </structure_exterieure>
    <structure_exterieure type="Organism">
      <libelle>Ecole des Ponts ParisTech</libelle>
    </structure_exterieure>
    <UR name="Rocquencourt"/>
    <keywords>
      <term>Data Assimilation</term>
      <term>Geophysics</term>
      <term>Image Processing</term>
      <term>Inverse Problem</term>
      <term>Stochastic Methods</term>
    </keywords>
    <moreinfo/>
  </identification>
  <team id="uid1">
    <person key="clime-2005-id18081">
      <firstname>Isabelle</firstname>
      <lastname>Herlin</lastname>
      <categoryPro>Chercheur</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, Team leader, Senior Researcher</moreinfo>
    </person>
    <person key="clime-2005-id18167">
      <firstname>Marc</firstname>
      <lastname>Bocquet</lastname>
      <categoryPro>Chercheur</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC, Deputy Director of CEREA, Senior Researcher</moreinfo>
      <hdr>oui</hdr>
    </person>
    <person key="clime-2005-id18368">
      <firstname>Vivien</firstname>
      <lastname>Mallet</lastname>
      <categoryPro>Chercheur</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, Researcher</moreinfo>
    </person>
    <person key="clime-2005-id18214">
      <firstname>Dominique</firstname>
      <lastname>Béréziat</lastname>
      <categoryPro>CollaborateurExterieur</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Univ. Paris VI, Associate Professor</moreinfo>
      <hdr>oui</hdr>
    </person>
    <person key="clime-2005-id18242">
      <firstname>Etienne</firstname>
      <lastname>Huot</lastname>
      <categoryPro>Enseignant</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Univ. Versailles Saint-Quentin-en-Yvelines, Associate Professor</moreinfo>
    </person>
    <person key="clime-2012-idp140574056078336">
      <firstname>Sylvain</firstname>
      <lastname>Doré</lastname>
      <categoryPro>Technique</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC</moreinfo>
    </person>
    <person key="clime-2011-idp140402885478368">
      <firstname>Raphaël</firstname>
      <lastname>Perillat</lastname>
      <categoryPro>Technique</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, granted by ADEME, until November 30</moreinfo>
    </person>
    <person key="clime-2010-id59812">
      <firstname>Anne</firstname>
      <lastname>Tilloy</lastname>
      <categoryPro>Technique</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, until September 21</moreinfo>
    </person>
    <person key="clime-2013-idp140610148035024">
      <firstname>Paul</firstname>
      <lastname>Baudin</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria</moreinfo>
    </person>
    <person key="clime-2009-id59717">
      <firstname>Karim</firstname>
      <lastname>Drifi</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, until April 30</moreinfo>
    </person>
    <person key="clime-2013-idp140610148039632">
      <firstname>Jean-Matthieu</firstname>
      <lastname>Haussaire</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC, from October 01</moreinfo>
    </person>
    <person key="clime-2012-idp140574056062016">
      <firstname>Yann</firstname>
      <lastname>Lepoittevin</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, granted by DGA</moreinfo>
    </person>
    <person key="clime-2013-idp140610148044240">
      <firstname>Jean</firstname>
      <lastname>Thorey</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC, from November 25</moreinfo>
    </person>
    <person key="clime-2010-id59714">
      <firstname>Victor</firstname>
      <lastname>Winiarek</lastname>
      <categoryPro>PhD</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC</moreinfo>
    </person>
    <person key="clime-2013-idp140610148048848">
      <firstname>Sylvain</firstname>
      <lastname>Girard</lastname>
      <categoryPro>PostDoc</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>IRSN, from February 04</moreinfo>
    </person>
    <person key="clime-2010-id59613">
      <firstname>Sergiy</firstname>
      <lastname>Zhuk</lastname>
      <categoryPro>Visiteur</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>IBM Research Dublin, Ireland, Researcher, from September 7 until October 9</moreinfo>
    </person>
    <person key="complex-2005-id18118">
      <firstname>Nathalie</firstname>
      <lastname>Gaudechoux</lastname>
      <categoryPro>Assistant</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria</moreinfo>
    </person>
    <person key="clime-2013-idp140610148055840">
      <firstname>Dehlinger</firstname>
      <lastname>Véronique</lastname>
      <categoryPro>Assistant</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>ENPC</moreinfo>
    </person>
    <person key="clime-2013-idp140610148058144">
      <firstname>Tristan</firstname>
      <lastname>Perotin</lastname>
      <categoryPro>AutreCategorie</categoryPro>
      <research-centre>Rocquencourt</research-centre>
      <moreinfo>Inria, Internship, from May 15 until November 14</moreinfo>
    </person>
  </team>
  <presentation id="uid2">
    <bodyTitle>Overall Objectives</bodyTitle>
    <subsection id="uid3" level="1">
      <bodyTitle>Clime in short</bodyTitle>
      <p>The international politic, economic and scientific contexts are pointing out the
role that is played by models and observation systems for forecasting and evaluating
environmental risks.</p>
      <p>The complexity of environmental phenomena as well as the operational
objectives of risk mitigation necessitate an intensive interweaving between
geophysical models, data processing, simulation, visualization and database
tools.</p>
      <p>For illustration purpose, we observe that this situation is met in the domain
of atmospheric pollution, whose modeling is gaining an ever-increasing
significance and impact, either at local (air quality), regional
(transboundary pollution) or global scale (greenhouse effect). In this
domain, numerical modeling systems are used for operational forecasts (short or long
term), detailed case studies, impact studies for industrial sites, as well
as coupled modeling, such as pollution and health or pollution and
economy. These scientific subjects strongly require linking/coupling the models with
all available data either of physical origin (e.g., models outputs), coming
from raw observations (satellite acquisitions and/or information measured
in situ by an observation network) or obtained by processing and
analysis of these observations (e.g., chemical concentrations retrieved by
inversion of a radiative transfer model).</p>
      <p>Clime has been jointly created, by Inria and École des Ponts ParisTech,
for studying these questions with researchers in data assimilation, image
processing, and modeling.</p>
      <p>Clime carries out research activities in three main areas:</p>
      <simplelist>
        <li id="uid4">
          <p noindent="true">Data assimilation methods: inverse modeling, network design, ensemble
methods, uncertainties estimation, uncertainties propagation.</p>
        </li>
        <li id="uid5">
          <p noindent="true">Image assimilation: assimilation of structures in environmental
forecasting models, study of ill-posed image processing problems with data
assimilation technics, definition of dynamic models from images, reduction of models.</p>
        </li>
        <li id="uid6">
          <p noindent="true">Development of integrated chains for data/models/outputs (system
architecture, workflow, database, visualization).</p>
        </li>
      </simplelist>
    </subsection>
  </presentation>
  <fondements id="uid7">
    <bodyTitle>Research Program</bodyTitle>
    <subsection id="uid8" level="1">
      <bodyTitle>Data assimilation and inverse modeling</bodyTitle>
      <p>This activity is one major concern of environmental
sciences. It matches up the setting and the use of data assimilation methods,
for instance variational methods (such as the 4D-Var method). An emerging issue lies in the
propagation of uncertainties by models, notably through ensemble forecasting
methods.</p>
      <p>Although modeling is not part of the scientific objectives of Clime, the
project-team has complete access to models developed by CEREA: the models from
Polyphemus (pollution forecasting from local to regional scales) and
Code_Saturne (urban scale). In regard to other modeling domains, such as
meteorology and oceanography, Clime
accesses models through co-operation initiatives.</p>
      <p>The research activities of Clime tackle scientific issues such as:</p>
      <simplelist>
        <li id="uid9">
          <p noindent="true">Within a family of models (differing by their physical formulations and
numerical approximations), which is the optimal model for a given set of
observations?</p>
        </li>
        <li id="uid10">
          <p noindent="true">How to reduce dimensionality of problems by Galerkin projection of
equations on subspaces? How to define these subspaces in order to keep the
main properties of systems?</p>
        </li>
        <li id="uid11">
          <p noindent="true">How to assess the quality of a forecast and its uncertainty? How do data quality, missing
data, data obtained from sub-optimal locations, affect the forecast? How to
better include information on uncertainties (of data, of models) within the
data assimilation system?</p>
        </li>
        <li id="uid12">
          <p noindent="true">How to make a forecast (and a better forecast!) by using several models
corresponding to different physical formulations? It also raises the
question: how should data be assimilated in this context?</p>
        </li>
        <li id="uid13">
          <p noindent="true">Which observational network should be set up to perform a better
forecast, while taking into account additional criteria such as observation
cost? What are the optimal location, type and mode of deployment of sensors?
How should trajectories of mobile sensors be operated, while the
studied phenomenon is evolving in time? This issue is usually referred as
“network design”.</p>
        </li>
      </simplelist>
    </subsection>
    <subsection id="uid14" level="1">
      <bodyTitle>Satellite acquisitions and image assimilation</bodyTitle>
      <p>In geosciences, the issue of coupling data, in particular satellite
acquisitions, and models is extensively studied for meteorology,
oceanography, chemistry-transport and land surface models. However,
satellite images are mostly assimilated on a point-wise basis. Three major approaches
arise if taking into account the spatial structures, whose displacement is
visualized on image sequences:</p>
      <simplelist>
        <li id="uid15">
          <p noindent="true">Image approach. Image assimilation allows the extraction of features
from image sequences, for instance motion field or structures' trajectory. A model of the dynamics is
considered (obtained by simplification of a geophysical model such as Navier-Stokes equations). An
observation operator is defined to express the links between the model state
and the pixels values. In the simplest case, the pixel value corresponds to
one coordinate of the model state and the observation operator is reduced to a
projection. However, in most cases, this operator is highly complex, implicit
and non-linear. Data assimilation techniques are developed to control the
initial state or the whole assimilation window. Image assimilation is also
applied to learn reduced models from image data and estimate a reliable and
small-size reconstruction of the dynamics, which is observed on the
sequence.</p>
        </li>
        <li id="uid16">
          <p noindent="true">Model approach. Image assimilation is used to control an environmental
model and obtain improved forecasts. In order to take into account the
spatial and temporal coherency of structures, specific image characteristics
are considered and dedicated norms and observation error covariances are
defined.</p>
        </li>
        <li id="uid17">
          <p noindent="true">Correcting a model. Another topic, mainly described for meteorology
in the literature, concerns the location of structures. How to force
the existence and to correct the location of structures in the model state
using image information? Most of the operational meteorological forecasting
institutes, such as MétéoFrance, UK-met, KNMI (in Netherlands), ZAMG (in
Austria) and Met-No (in Norway), study this issue because operational
forecasters often modify their forecasts based on visual comparisons between the
model outputs and the structures displayed on satellite images.</p>
        </li>
      </simplelist>
    </subsection>
    <subsection id="uid18" level="1">
      <bodyTitle>Software chains for environmental
applications</bodyTitle>
      <p>An objective of Clime is to participate in the design and creation of software
chains for impact assessment and environmental crisis management. Such
software chains bring together static or dynamic databases, data assimilation
systems, forecast models, processing methods for environmental data and
images, complex visualization tools, scientific workflows, ...</p>
      <p>Clime is currently building, in partnership with École des Ponts ParisTech and EDF R&amp;D, such a system for air pollution modeling: Polyphemus (see the web
site
<ref xlink:href="http://cerea.enpc.fr/polyphemus/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>cerea.<allowbreak/>enpc.<allowbreak/>fr/<allowbreak/>polyphemus/</ref>),
whose architecture is specified to satisfy data requirements (e.g.,
various raw data natures and sources, data preprocessing) and to support
different uses of an air quality model (e.g., forecasting, data assimilation,
ensemble runs).</p>
    </subsection>
  </fondements>
  <domaine id="uid19">
    <bodyTitle>Application Domains</bodyTitle>
    <subsection id="uid20" level="1">
      <bodyTitle>Introduction</bodyTitle>
      <p>The central application domain of the project-team is atmospheric chemistry.
We develop and maintain the air quality modeling system Polyphemus, which
includes several numerical models (Gaussian models, Lagrangian model, two 3D
Eulerian models including Polair3D) and their adjoints, and different high
level methods: ensemble forecast, sequential and variational data assimilation
algorithms. Advanced data assimilation methods, network design, inverse modeling,
ensemble forecast are studied in the context of air chemistry. Note that
addressing these high level issues requires controlling the full software
chain (models and data assimilation algorithms).</p>
      <p>The activity on assimilation of satellite data is mainly carried out for
meteorology and oceanography. This is addressed in cooperation with external
partners who provide numerical models. Concerning oceanography, the aim is
to assess ocean surface circulation, by assimilating fronts and
vortices displayed on image acquisitions. Concerning meteorology, the focus is on
correcting the model location of structures related to high-impact weather
events (cyclones, convective storms, etc.) by assimilating
images.</p>
    </subsection>
    <subsection id="uid21" level="1">
      <bodyTitle>Air quality</bodyTitle>
      <p>Air quality modeling implies studying the interactions between meteorology and
atmospheric chemistry in the various phases of matter, which leads to the
development of highly complex models. The different usages of these models
comprise operational forecasting, case studies, impact studies, etc.,
with both societal (e.g., public information on pollution forecast) and
economical impacts (e.g., impact studies for dangerous industrial
sites). Models lack some appropriate data, for instance better emissions, to
perform an accurate forecast and data assimilation techniques are recognized
as a major key point for improving forecast's quality.</p>
      <p>In this context, Clime is interested in various problems, the following being
the crucial ones:</p>
      <simplelist>
        <li id="uid22">
          <p noindent="true">The development of ensemble forecast methods for estimating the quality
of the prediction, in relation with the quality of the model and the
observations. This allows sensitivity analysis with respect to the model's parameters so
as to identify physical and chemical processes, whose modeling must be
improved.</p>
        </li>
        <li id="uid23">
          <p noindent="true">The development of methodologies for sequential aggregation of ensemble
simulations. What ensembles should be generated for that purpose, how
spatialized forecasts can be generated with aggregation, how can the
different approaches be coupled with data assimilation?</p>
        </li>
        <li id="uid24">
          <p noindent="true">The definition of second-order data assimilation methods for the design
of optimal observation networks. The two main objectives are: management of combinations of sensor types
and deployment modes and dynamic management of mobile sensors' trajectories.</p>
        </li>
        <li id="uid25">
          <p noindent="true">How to estimate the emission rate of an accidental release of a
pollutant, using observations and a dispersion model (from the near-field to
the continental scale)? How to optimally predict the evolution of a plume?
Hence, how to help people in charge of risk evaluation for the population?</p>
        </li>
        <li id="uid26">
          <p noindent="true">The definition of non-Gaussian approaches for data assimilation.</p>
        </li>
        <li id="uid27">
          <p noindent="true">The assimilation of satellite measurements of troposphere chemistry.</p>
        </li>
      </simplelist>
      <p>The activities of Clime in air quality are supported by the development of the
Polyphemus air quality modeling system. This system has a modular design, which
makes it easier to manage high level applications such as inverse modeling,
data assimilation and ensemble forecast.</p>
    </subsection>
    <subsection id="uid28" level="1">
      <bodyTitle>Oceanography</bodyTitle>
      <p>The capacity of performing a high quality forecast of the state of the ocean,
from the regional to the global scales, is of major interest. Such a forecast
can only be obtained by systematically coupling numerical models and
observations (in situ and satellite data). In this context, being able
to assimilate image structures becomes a key point. Examples of such image
structures are:</p>
      <simplelist>
        <li id="uid29">
          <p noindent="true">apparent motion that represents surface velocity;</p>
        </li>
        <li id="uid30">
          <p noindent="true">trajectories, obtained either from tracking of features or from
integration of the velocity field;</p>
        </li>
        <li id="uid31">
          <p noindent="true">spatial objects, such as fronts, eddies or filaments.</p>
        </li>
      </simplelist>
      <p>Image models of these structures are developed and take into account the
underlying physical processes. Image data are assimilated in these image
models to derive pseudo-observations of state variables, which are further
assimilated in numerical ocean forecast models.</p>
    </subsection>
    <subsection id="uid32" level="1">
      <bodyTitle>Meteorology</bodyTitle>
      <p>Meteorological forecasting constitutes a major applicative challenge for image
assimilation. Although satellite data are operationally assimilated within
models, this is mainly done on an independent pixel basis: the observed
radiance is linked to the state variables via a radiative transfer model, that
plays the role of an observation operator. Indeed, because of their limited
spatial and temporal resolutions, numerical weather forecast models fail to
exploit image structures, such as precursors of high impact weather:</p>
      <simplelist>
        <li id="uid33">
          <p noindent="true">cyclogenesis related to the intrusion of dry stratospheric air in the
troposphere (a precursor of cyclones),</p>
        </li>
        <li id="uid34">
          <p noindent="true">convective systems (supercells) leading to heavy winter time storms,</p>
        </li>
        <li id="uid35">
          <p noindent="true">low-level temperature inversion leading to fog and ice formation,
etc.</p>
        </li>
      </simplelist>
      <p>To date, there is no available method for assimilating such data, which are
characterized by a strong coherence in space and time. Meteorologists have
developed qualitative Conceptual Models (CMs), for describing the high impact
weathers and their signature on images, and tools to detect CMs on image
data. The result of this detection is used for correcting the numerical
models, for instance by modifying the initialization. The aim is therefore to
develop a methodological framework allowing to assimilate the detected CMs
within numerical forecast models. This is a challenging issue given the
considerable impact of the related meteorological events.</p>
    </subsection>
  </domaine>
  <logiciels id="uid36">
    <bodyTitle>Software and Platforms</bodyTitle>
    <subsection id="uid37" level="1">
      <bodyTitle>
        <ref xlink:href="http://cerea.enpc.fr/polyphemus/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">Polyphemus</ref>
      </bodyTitle>
      <participants>
        <person key="clime-2012-idp140574056078336">
          <firstname>Sylvain</firstname>
          <lastname>Doré</lastname>
        </person>
        <person key="clime-2005-id18368">
          <firstname>Vivien</firstname>
          <lastname>Mallet</lastname>
        </person>
        <person key="PASUSERID">
          <firstname>Florian</firstname>
          <lastname>Couvidat</lastname>
          <moreinfo>CEREA</moreinfo>
        </person>
        <person key="PASUSERID">
          <firstname>Yiguo</firstname>
          <lastname>Wang</lastname>
          <moreinfo>CEREA</moreinfo>
        </person>
        <person key="PASUSERID">
          <firstname>Nora</firstname>
          <lastname>Duhanyan</lastname>
          <moreinfo>CEREA</moreinfo>
        </person>
        <person key="PASUSERID">
          <firstname>Yelva</firstname>
          <lastname>Roustan</lastname>
          <moreinfo>CEREA</moreinfo>
        </person>
      </participants>
      <p>Polyphemus (see the web site
<ref xlink:href="http://cerea.enpc.fr/polyphemus/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>cerea.<allowbreak/>enpc.<allowbreak/>fr/<allowbreak/>polyphemus/</ref>)
is a modeling system for air quality. As such, it is designed to yield
up-to-date simulations in a reliable framework: data assimilation, ensemble
forecast and daily forecasts. Its completeness makes it suitable for use in
many applications: photochemistry, aerosols, radionuclides, etc. It
is able to handle simulations from local to continental scales, with several
physical models. It is divided into three main parts:</p>
      <simplelist>
        <li id="uid38">
          <p noindent="true">libraries that gather data processing tools (SeldonData), physical
parameterizations (AtmoData) and postprocessing abilities (AtmoPy);</p>
        </li>
        <li id="uid39">
          <p noindent="true">programs for physical preprocessing and chemistry-transport models
(Polair3D, Castor, two Gaussian models, a Lagrangian model);</p>
        </li>
        <li id="uid40">
          <p noindent="true">model drivers and observation modules for model coupling, ensemble forecasting and data assimilation.</p>
        </li>
      </simplelist>
      <p>Figure <ref xlink:href="#uid41" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> depicts a typical result produced by Polyphemus.</p>
      <object id="uid41">
        <table>
          <tr>
            <td>
              <ressource xlink:href="IMG/uncertainty.png" type="float" width="256.0748pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
            </td>
          </tr>
        </table>
        <caption>Map of the relative standard deviation (or spread, %) of an
ensemble built with
Polyphemus (ozone simulations, <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mi>μ</mi><mrow/><mi>g</mi><mspace width="0.277778em"/><msup><mi>m</mi><mrow><mo>-</mo><mn>3</mn></mrow></msup></mrow></math></formula>). The standard
deviations are
averaged over the summer of 2001. They provide an estimation of the
simulation uncertainties.</caption>
      </object>
      <p>Clime is involved in the overall design of the system and in the development
of advanced methods in model coupling, data assimilation and uncertainty quantification
(through model drivers and post-processing).</p>
      <p>In 2013, Polyphemus has received numerous improvements on aerosol modeling, including better dynamics for organic aerosol formation and interactions between organic and inorganic aerosols. The data assimilation part of Polyphemus can now perform 3D data assimilation, taking advantage of Lidar data. Further integration of the data assimilation library Verdandi was also carried out.</p>
    </subsection>
    <subsection id="uid42" level="1">
      <bodyTitle>
        <ref xlink:href="http://verdandi.gforge.inria.fr/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">Data assimilation library: Verdandi</ref>
      </bodyTitle>
      <participants>
        <person key="clime-2005-id18368">
          <firstname>Vivien</firstname>
          <lastname>Mallet</lastname>
        </person>
        <person key="PASUSERID">
          <firstname>Dominique</firstname>
          <lastname>Chapelle</lastname>
          <moreinfo>M3DISIM</moreinfo>
        </person>
        <person key="PASUSERID">
          <firstname>Philippe</firstname>
          <lastname>Moireau</lastname>
          <moreinfo>M3DISIM</moreinfo>
        </person>
        <person key="clime-2010-id59812">
          <firstname>Anne</firstname>
          <lastname>Tilloy</lastname>
        </person>
        <person key="clime-2013-idp140610148035024">
          <firstname>Paul</firstname>
          <lastname>Baudin</lastname>
        </person>
        <person key="clime-2013-idp140610148058144">
          <firstname>Tristan</firstname>
          <lastname>Perotin</lastname>
        </person>
      </participants>
      <p>The leading idea is to develop a data assimilation library intended to be
generic, at least for high-dimensional systems. Data assimilation methods,
developed and used by several teams at Inria, are generic enough to be coded
independently of the system to which they are applied. Therefore these methods
can be put together in a library aiming at:</p>
      <simplelist>
        <li id="uid43">
          <p noindent="true">making easier the application of methods to a great number of problems,</p>
        </li>
        <li id="uid44">
          <p noindent="true">making the developments perennial and sharing them,</p>
        </li>
        <li id="uid45">
          <p noindent="true">improving the broadcast of data assimilation works.</p>
        </li>
      </simplelist>
      <p>An object-oriented language (C++) has been chosen for the core of the
library. A high-level interface to Python is automatically built. The design study
raised many questions, related to high dimensional scientific computing, the
limits of the object contents and their interfaces. The chosen object-oriented
design is mainly based on three class hierarchies: the methods, the
observation managers and the models. Several base facilities have also been
included, for message exchanges between the objects, output saves, logging
capabilities, computing with sparse matrices.</p>
      <p>In 2013, version 1.5 was released with better consistency between the methods. Verdandi received improvements in its test cases. Increased flexibility was introduced in error descriptions, especially for uncertainty quantification.</p>
      <p>A C++ interface to the Nucleus for European Modelling of the Ocean
(see the web site NEMO <ref xlink:href="http://www.nemo-ocean.eu/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>nemo-ocean.<allowbreak/>eu/</ref>) has been developed so that it can be plugged to Verdandi. The
interface currently enables the application of Monte Carlo simulations
and the ensemble Kalman filter.
</p>
    </subsection>
    <subsection id="uid46" level="1">
      <bodyTitle>Urban air quality analysis</bodyTitle>
      <participants>
        <person key="clime-2010-id59812">
          <firstname>Anne</firstname>
          <lastname>Tilloy</lastname>
        </person>
        <person key="clime-2005-id18368">
          <firstname>Vivien</firstname>
          <lastname>Mallet</lastname>
        </person>
        <person key="PASUSERID">
          <firstname>Raphaël</firstname>
          <lastname>Périllat</lastname>
        </person>
      </participants>
      <p>“Urban Air Quality Analysis” carries out data assimilation at urban scale.
It merges the outputs of a numerical model (maps of pollutant concentrations)
with observations from an air quality monitoring network, in order to produce
the so-called analyses, that is, corrected concentration maps. The data
assimilation computes the Best Linear Unbiased Estimator (BLUE), with a call
to the data assimilation library Verdandi. The error covariance matrices are
parameterized for both model simulations and observations. For the model state
error covariances, the parameterization primarily relies on the road network.
The software handles ADMS Urban output files, for a posteriori analyses or in an
operational context.</p>
      <p>In 2013, the software introduced new models for error covariances. It may now take into account tunnels. New options were added to filter out certain observations. The software was extended to handle new file formats.</p>
    </subsection>
  </logiciels>
  <resultats id="uid47">
    <bodyTitle>New Results</bodyTitle>
    <subsection id="uid48" level="1">
      <bodyTitle>New methods for data assimilation</bodyTitle>
      <p>One major objective of Clime is the conception of new techniques for data assimilation in
geophysical sciences. Clime is active on several of the most challenging theoretical aspects of
data assimilation: data assimilation methods based on non-Gaussian assumptions, methods for
estimating errors, ensemble filtering techniques, 4D variational assimilation approaches,
ensemble-variational methods, etc.</p>
      <p>This year, focus was on ensemble-variational methods. We introduced a new method known
as the iterative ensemble Kalman smoother. It is an ensemble method with an underlying cost
function; it does not require the use of the adjoint; and it is flow-dependent. Because of these
propreties, the IEnKS outperforms other data assimilation methods when tested with perfect
meteorological toy-models. Its potential for parameter estimation has also been demonstrated.</p>
      <subsection id="uid49" level="2">
        <bodyTitle>An iterative ensemble Kalman smoother</bodyTitle>
        <participants>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Pavel</firstname>
            <lastname>Sakov</lastname>
            <moreinfo>BOM, Australia</moreinfo>
          </person>
        </participants>
        <p>The iterative ensemble Kalman filter (IEnKF) was recently proposed to improve the performance of
ensemble Kalman filtering with strongly nonlinear geophysical models. IEnKF can be used as a
lag-one smoother and extended to a fixed-lag smoother: the iterative ensemble Kalman smoother
(IEnKS <ref xlink:href="#clime-2013-bid0" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>). IEnKS is an ensemble variational method. It does not require the use of the tangent
linear of the evolution and observation models, nor the adjoint of these models: the required
sensitivities (gradient and Hessian) are obtained from the ensemble. Looking for the optimal
performance, we consider a quasi-static algorithm, out of the many possible extensions. IEnKS
is explored on the Lorenz'95 model and on a 2D turbulence model. As a logical extension of
IEnKF, IEnKS significantly outperforms standard Kalman filters and smoothers in strongly
nonlinear regimes. In mildly nonlinear regimes (typically synoptic scale meteorology), its
filtering performance is marginally but clearly better than the standard ensemble Kalman filter, and
it keeps improving as the length of the temporal data assimilation window is increased. For long
windows, its smoothing performance very significantly outranks the standard smoothers, which is
believed to stem from the variational but flow-dependent nature of the algorithm. For very long
windows, the use of a multiple data assimilation variant of the scheme, where observations are
assimilated several times, is advocated. This paves the way for finer re-analysis freed from the
static prior assumption of 4D-Var, but also partially freed from the Gaussian assumptions that
usually impede standard ensemble Kalman filtering and smoothing.</p>
      </subsection>
      <subsection id="uid50" level="2">
        <bodyTitle>Joint state and parameter estimation with an iterative ensemble Kalman smoother</bodyTitle>
        <participants>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Pavel</firstname>
            <lastname>Sakov</lastname>
            <moreinfo>BOM, Australia</moreinfo>
          </person>
        </participants>
        <p>Both ensemble filtering and variational data assimilation methods have proven
being useful in the joint
estimation of state variables and parameters of geophysical models. Yet, their respective benefits
and drawbacks in this task are distinct. An ensemble variational method, known as the iterative
ensemble Kalman smoother (IEnKS), has recently been introduced. It is based on an adjoint-free
variational but flow-dependent scheme. As such, IEnKS is a candidate tool for joint state and
parameter estimation that may inherit the benefits from both the ensemble filtering and variational
approaches.</p>
        <p>In this study <ref xlink:href="#clime-2013-bid1" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, an augmented state IEnKS is tested on the estimation of the forcing parameter of the
Lorenz'95 model. Since joint state and parameter estimation is especially useful in applications
where the forcings are uncertain but nevertheless determining, typically in atmospheric chemistry,
the augmented state IEnKS is tested on a new low-order model that combines the Lorenz'95 model,
representing its meteorological part, and the advection diffusion of a tracer for its chemical part.
In these experiments, IEnKS is compared to the ensemble Kalman filter, the ensemble Kalman
smoother and a 4D-Var method, that are considered choices to solve these joint
estimation problems. In this low-order model context, IEnKS is shown to significantly outperform those
methods, for any length of the data assimilation window, and for present time analysis as well as
retrospective analysis. Besides, the performance of IEnKS is even more striking on parameter
estimation, whereas getting close to the same performance with 4D-Var is likely to require both a
long data assimilation window and a complex modeling of the background statistics.</p>
      </subsection>
      <subsection id="uid51" level="2">
        <bodyTitle>Data assimilation applied to air quality at urban scale</bodyTitle>
        <participants>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Raphaël</firstname>
            <lastname>Périllat</lastname>
          </person>
          <person key="clime-2010-id59812">
            <firstname>Anne</firstname>
            <lastname>Tilloy</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Fabien</firstname>
            <lastname>Brocheton</lastname>
            <moreinfo>Numtech</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>David</firstname>
            <lastname>Poulet</lastname>
            <moreinfo>Numtech</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Frédéric</firstname>
            <lastname>Mahé</lastname>
            <moreinfo>Airparif</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Pierre</firstname>
            <lastname>Pernot</lastname>
            <moreinfo>Airparif</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Fabrice</firstname>
            <lastname>Joly</lastname>
            <moreinfo>Airparif</moreinfo>
          </person>
        </participants>
        <p>Based on Verdandi <ref xlink:href="#clime-2013-bid2" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, Polyphemus and the “Urban Air Quality Analysis” software,
data assimilation was further developed at urban scale. The Best Linear
Unbiased Estimator (BLUE) is computed to merge the outputs of the ADMS Urban
model and the observations of a sparse monitoring network <ref xlink:href="#clime-2013-bid3" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>. We improved the
modeling of the covariance of the model state error. The assimilation was
applied for part of Paris (see Fig. <ref xlink:href="#uid52" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>) and for Paris region, in
the context of the PRIMEQUAL project PREQUALIF (“Multidisciplinary Program on
Air Quality Research in Île-de-France”).</p>
        <object id="uid52">
          <table>
            <tr>
              <td>
                <ressource xlink:href="IMG/adms_2012-09-01_18.png" type="inline" width="125.19194pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td>
                <ressource xlink:href="IMG/analyse_2012-09-01_18.png" type="inline" width="125.19194pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
            </tr>
          </table>
          <caption>Left: Map of [NO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula>] (<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mi>μ</mi><mrow/><mi>g</mi><mspace width="4pt"/><msup><mi>m</mi><mrow><mo>-</mo><mn>3</mn></mrow></msup></mrow></math></formula>), before assimilation, at a given date in September 2012. Right: Map of [NO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula>] (<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mi>μ</mi><mrow/><mi>g</mi><mspace width="4pt"/><msup><mi>m</mi><mrow><mo>-</mo><mn>3</mn></mrow></msup></mrow></math></formula>), after assimilation of the observations (disks).</caption>
        </object>
        <p>It was applied to nitrogen dioxide, particulate matter and black carbon. Specific investigations were carried out to estimate the variance of the a posteriori error and to determine the impact of each monitoring station on the final results.</p>
      </subsection>
    </subsection>
    <subsection id="uid53" level="1">
      <bodyTitle>Inverse modeling</bodyTitle>
      <p>We continued research on inverse modelling techniques, with a focus on hyperparameter estimation
when the statistics are non-Gaussian. We applied these methods to the estimation of the caesium-137 Fukushima
source term using heterogenous datasets. We applied similar methods to the estimation of Volatile
Organic Compounds (VOC) at the European scale by assimilation of the EMEP VOC observations over one
year. We also studied the estimation of several hyperparameters in the context of CO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula> flux inversions.</p>
      <subsection id="uid54" level="2">
        <bodyTitle>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</bodyTitle>
        <participants>
          <person key="clime-2010-id59714">
            <firstname>Victor</firstname>
            <lastname>Winiarek</lastname>
          </person>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Nora</firstname>
            <lastname>Duhanyan</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Yelva</firstname>
            <lastname>Roustan</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Olivier</firstname>
            <lastname>Saunier</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Anne</firstname>
            <lastname>Mathieu</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
        </participants>
        <p>To estimate the amount of radionuclides and the temporal profile of the source term released in the
atmosphere during the accident of the Fukushima Daiichi nuclear power plant in March 2011, inverse
modeling techniques have been used and have proven their ability in this context. In a previous study,
the lower bounds of the caesium-137 and iodine-131 source terms were estimated with such techniques,
using activity concentration observations. The importance of an objective assessment of prior
errors (the observation errors and the background errors) was emphasised for a reliable inversion.
In such critical context where the meteorological conditions can make the source term partly
unobservable and where only a few observations are available, such prior estimation techniques are
mandatory, the retrieved source term being very sensitive to this estimation.</p>
        <p>We propose to extend the use of these techniques to the estimation of prior errors when assimilating
observations from several data sets <ref xlink:href="#clime-2013-bid4" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>. The aim is to compute an estimate of the caesium-137 source
term jointly using all available data about this radionuclide, such as activity concentrations in
the air, but also daily fallout measurements and total cumulated fallout measurements. It is crucial
to properly and simultaneously estimate the background errors and the prior errors relative to each
data set. A proper estimation of prior errors is also a necessary condition to reliably estimate the
a posteriori uncertainty of the estimated source term. Using such techniques, we retrieve a total
released quantity of caesium-137 in the interval <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mn>11</mn><mo>.</mo><mn>6</mn><mo>-</mo><mn>19</mn><mo>.</mo><mn>3</mn></mrow></math></formula> PBq with an estimated standard
deviation range of <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mn>15</mn><mo>-</mo><mn>20</mn><mo>%</mo></mrow></math></formula> depending on the method and the data sets. The “blind” time
intervals of the source term have also been strongly mitigated compared to the first estimations
with only activity concentration data.</p>
      </subsection>
      <subsection id="uid55" level="2">
        <bodyTitle>An inverse modeling method to assess the source term of the
Fukushima Nuclear Power Plant accident using gamma dose rate observations</bodyTitle>
        <participants>
          <person key="PASUSERID">
            <firstname>Olivier</firstname>
            <lastname>Saunier</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Anne</firstname>
            <lastname>Mathieu</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Damien</firstname>
            <lastname>Didier</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Maryline</firstname>
            <lastname>Tombette</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Denis</firstname>
            <lastname>Quélo</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="clime-2010-id59714">
            <firstname>Victor</firstname>
            <lastname>Winiarek</lastname>
          </person>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
        </participants>
        <p>The Chernobyl nuclear accident, and more recently the Fukushima accident, highlighted that the
largest source of error on consequences assessment is the source term, including the time evolution
of the release rate and its distribution between radioisotopes. Inverse modeling methods, which
combine environmental measurements and atmospheric dispersion models, have
proven being efficient in
assessing source term due to an accidental situation. Most existing approaches are designed to use air
sampling measurements and some of them also use deposition measurements <ref xlink:href="#clime-2013-bid4" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>. Some studies have been conceived to use dose rate
measurements, but none of the developed methods were carried out to assess the complex source term of a real
accident situation like the Fukushima accident. However, dose rate measurements are generated by the
most widespread measurement system and, in the event of a nuclear accident, these data constitute
the main source of measurements of the plume and radioactive fallout during releases. This study <ref xlink:href="#clime-2013-bid5" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, <ref xlink:href="#clime-2013-bid6" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>
proposes a method to use dose rate measurements as part of an inverse modeling approach to assess
source terms. The method is proven efficient and reliable when applied to the accident at the
Fukushima Daiichi Nuclear Power Plant (FD-NPP). The emissions for the eight main isotopes
have been assessed. Accordingly, 105.9 PBq of <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>131</mn></msup></math></formula>I, 35.8 PBq of <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>132</mn></msup></math></formula>I, 15.5 PBq of
<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>137</mn></msup></math></formula>Cs and 12,134 PBq of noble gases were released. The events at FD-NPP (such as venting,
explosions, etc.) known to have caused atmospheric releases are well identified in the retrieved
source term. The estimated source term is validated by comparing simulations of atmospheric
dispersion and deposition with environmental observations. In total, it was found that for 80 % of
the measurements, simulated and observed dose rates agreed within a factor of 2. Changes in dose
rates over time have been overall properly reconstructed, especially in the most contaminated areas
to the northwest and south of the FD-NPP. A comparison with observed atmospheric activity
concentration and surface deposition shows that the emissions of caesiums and <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>131</mn></msup></math></formula>I are
realistic but that <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>132</mn></msup></math></formula>I and <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mrow/><mn>132</mn></msup></math></formula>Te are probably underestimated and noble gases are likely
overestimated. Finally, an important outcome of this study is that the method proved to be
perfectly suited to emergency management and could contribute to improve emergency response in the
event of a nuclear accident.</p>
      </subsection>
      <subsection id="uid56" level="2">
        <bodyTitle>Estimation of volatile organic compound emissions for Europe using data assimilation</bodyTitle>
        <participants>
          <person key="PASUSERID">
            <firstname>Mohammad Reza</firstname>
            <lastname>Koohkan</lastname>
          </person>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Yelva</firstname>
            <lastname>Roustan</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Yougseob</firstname>
            <lastname>Kim</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Christian</firstname>
            <lastname>Seigneur</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
        </participants>
        <p>The emissions of non-methane volatile organic compounds (VOCs) over western Europe for the year 2005
are estimated via inverse modeling by assimilation of in situ observations of concentration and
they are subsequently compared to a standard emission inventory. The study <ref xlink:href="#clime-2013-bid7" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> focuses on fifteen VOC
species: five aromatics, six alkanes, two alkenes, one alkyne and one biogenic diene. The inversion
relies on a validated fast adjoint of the chemical transport model used to simulate the fate and
transport of these VOCs. The assimilated ground-based measurements over Europe are provided by the
European Monitoring and Evaluation Programme (EMEP) network. The background emissions errors and
the prior observational errors are estimated by maximum likelihood approaches. The positivity
assumption on the VOC emission fluxes is pivotal for a successful inversion and this maximum
likelihood approach consistently accounts for the positivity of the fluxes. For most species, the
retrieved emissions lead to a significant reduction of the bias, which underlines the misfit between
the standard inventories and the observed concentrations. The results are validated through a
forecast test and a cross-validation test. An estimation of the posterior uncertainty is also
provided. It is shown that the statistically consistent non-Gaussian approach, based on a reliable
estimation of the errors, offers the best performance. The efficiency in correcting the inventory
depends on the lifetime of the VOCs and the accuracy of the boundary conditions. In particular, it
is shown that the use of in situ observations using a sparse monitoring network to estimate
emissions of isoprene is inadequate because its short chemical lifetime significantly limits the
spatial radius of influence of the monitoring data. For species with longer lifetime (a few days),
successful, albeit partial, emission corrections can reach regions hundreds of kilometres away from
the stations. Domainwide corrections of the emissions inventories of some VOCs are significant,
with underestimations on the order of a factor of two for propane, ethane, ethylene and acetylene.</p>
      </subsection>
      <subsection id="uid57" level="2">
        <bodyTitle>Hyperparameter estimation for uncertainty quantification in mesoscale carbon dioxide inversions</bodyTitle>
        <participants>
          <person key="PASUSERID">
            <firstname>Lin</firstname>
            <lastname>Wu</lastname>
            <moreinfo>LSCE, France</moreinfo>
          </person>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Frédéric</firstname>
            <lastname>Chevallier</lastname>
            <moreinfo>LSCE, France</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Thomas</firstname>
            <lastname>Lauvaux</lastname>
            <moreinfo>Department of Meteorology, Pennsylvania State University, USA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Kenneth</firstname>
            <lastname>Davies</lastname>
            <moreinfo>Department of Meteorology, Pennsylvania State University, USA</moreinfo>
          </person>
        </participants>
        <p>Uncertainty quantification is critical in the inversion of CO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula> surface fluxes from atmospheric
concentration measurements. We estimate the main hyperparameters of the error covariance
matrices for a priori fluxes and CO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula> concentrations, that is, the variances and the correlation
lengths, using real, continuous hourly CO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula> concentration data in the context of the Ring 2
experiment of the North American Carbon Program Mid Continent Intensive. Several criteria, namely
maximum likelihood (ML), general cross-validation (GCV) and <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mi>χ</mi><mn>2</mn></msup></math></formula> test are compared for the first
time under a realistic setting in a mesoscale CO<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>2</mn></msub></math></formula> inversion. It is shown <ref xlink:href="#clime-2013-bid8" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> that the optimal
hyperparameters under the ML criterion assure perfect <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mi>χ</mi><mn>2</mn></msup></math></formula> consistency of the inverted
fluxes. Inversions using the ML error variances estimates rather than the prescribed default values
are less weighted by the observations, because the default values underestimate the model-data
mismatch error, which is assumed to be dominated by the atmospheric transport error. As for the
spatial correlation length in prior flux errors, the Ring 2 network is sparse for GCV and this
method fails to reach an optimum. In contrast, the ML estimate (e.g. an optimum of 20 km for the
first week of June 2007) does not support long spatial correlations that are usually assumed in the
default values.</p>
      </subsection>
    </subsection>
    <subsection id="uid58" level="1">
      <bodyTitle>Monitoring network design</bodyTitle>
      <p>In this section, we report studies that are related to the evaluation of monitoring networks and to
new monitoring strategies. This year, we studied the impact of using lidar observation for
particulate matter forecasting.</p>
      <subsection id="uid59" level="2">
        <bodyTitle>Assimilation of ground versus lidar observations for
PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula> forecasting</bodyTitle>
        <participants>
          <person key="PASUSERID">
            <firstname>Yiguo</firstname>
            <lastname>Wang</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Karine</firstname>
            <lastname>Sartelet</lastname>
            <moreinfo>CEREA</moreinfo>
          </person>
          <person key="clime-2005-id18167">
            <firstname>Marc</firstname>
            <lastname>Bocquet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Patrick</firstname>
            <lastname>Chazette</lastname>
            <moreinfo>LSCE, France</moreinfo>
          </person>
        </participants>
        <p>This study <ref xlink:href="#clime-2013-bid9" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> investigates the potential impact of future ground-based lidar networks on analysis and
short-term forecasts of PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula>. To do so, an Observing System Simulation Experiment (OSSE) is
built for PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula> data assimilation using optimal interpolation over Europe for one month in 2001.
First, we estimate the efficiency of the assimilation of lidar network measurements in improving
PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula> concentration analysis and forecast. It is compared to the efficiency of assimilating
concentration measurements from the AirBase ground network, which includes about 500 stations in
western Europe. It is found that the assimilation of lidar observations is more efficient at
improving PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula> concentrations in terms of root mean square error and correlation after 12
hours of assimilation than the assimilation of AirBase measurements. Moreover, the spatial and
temporal influence of the assimilation of lidar observations is larger and longer. In our
experiments, the assimilation of lidar products improves PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula> forecast for 108 hours against
60 hours for AirBase assimilation. The results show a potentially powerful impact of the future
lidar networks. Secondly, since a lidar is a very costly instrument, a sensitivity study on the
number of required lidars is performed to help defining an optimal lidar network for PM<formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msub><mrow/><mn>10</mn></msub></math></formula>
forecast. The results suggest 12 lidar stations over western Europe, because a network with 26
lidar stations is more expensive and offers a limited improvement (less than <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><mn>1</mn><mspace width="4pt"/><mi>μ</mi><mi>g</mi><mspace width="4pt"/><msup><mi>m</mi><mrow><mo>-</mo><mn>3</mn></mrow></msup></mrow></math></formula> of
root mean square error on average) over the lidar network. A comparison of two networks with
12 lidar stations at different locations does not lead to substantial differences.</p>
      </subsection>
    </subsection>
    <subsection id="uid60" level="1">
      <bodyTitle>Reduction and emulation</bodyTitle>
      <p>The use of environmental models raise a number of problems due to:</p>
      <simplelist>
        <li id="uid61">
          <p noindent="true">the dimension of the inputs, which can easily be <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><msup><mn>10</mn><mn>5</mn></msup><mo>-</mo><mo>-</mo><msup><mn>10</mn><mn>8</mn></msup></mrow></math></formula> at every time step;</p>
        </li>
        <li id="uid62">
          <p noindent="true">the dimension of the state vector, which is usually <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mrow><msup><mn>10</mn><mn>5</mn></msup><mo>-</mo><mo>-</mo><msup><mn>10</mn><mn>7</mn></msup></mrow></math></formula>;</p>
        </li>
        <li id="uid63">
          <p noindent="true">the high computational cost.</p>
        </li>
      </simplelist>
      <p>In particular, the application of data assimilation methods and uncertainty quantification techniques may require dimension reduction and cost reduction. The dimension reduction consists in projecting the inputs and the state vector to low-dimensional subspaces. The cost reduction can be carried out by emulation, i.e., the replacement of costly components with fast surrogates.</p>
      <subsection id="uid64" level="2">
        <bodyTitle>Reduction and emulation of a chemistry-transport model</bodyTitle>
        <participants>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Serge</firstname>
            <lastname>Guillas</lastname>
            <moreinfo>University College London</moreinfo>
          </person>
        </participants>
        <p>Both reduction and emulation were applied to the dynamic air quality model
Polair3D from Polyphemus. The reduction relied on proper orthogonal
decomposition (POD) on the input data and on the state vector. The dimension of the reduced subspace for the input data is about 80, while the dimension of the reduced state vector is less than 10. The projection of the state vector on its reduced subspace can be carried out before every integration time step, so that one can reproduce a full state trajectory (in time) using the reduced model.</p>
        <p>Significant advances were made to emulate the reduced model, which requires about 90 inputs (reduced input data and reduced state vector) and computes about 10 outputs (reduced state vector). 90 inputs is however a large number to build an emulator using a classical approaches. Promising results were however obtained with radial basis functions and an adapted kriging-based method.</p>
      </subsection>
      <subsection id="uid65" level="2">
        <bodyTitle>Reduction and emulation of a static air quality model</bodyTitle>
        <participants>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="clime-2010-id59812">
            <firstname>Anne</firstname>
            <lastname>Tilloy</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Fabien</firstname>
            <lastname>Brocheton</lastname>
            <moreinfo>Numtech</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>David</firstname>
            <lastname>Poulet</lastname>
            <moreinfo>Numtech</moreinfo>
          </person>
        </participants>
        <p>The dimension reduction was applied to the outputs of the urban air quality
model ADMS Urban, which is a static model with low-dimensional inputs and
high-dimensional outputs. A proper orthogonal decomposition (POD) on the outputs
allowed us to drastically reduce their dimension, from <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><msup><mn>10</mn><mn>4</mn></msup></math></formula> to just a few
scalars. The emulation of the reduced model itself was successfully carried out with radial basis functions or an adapted kriging-based method. The resulting reduced/emulated model exhibited meaningful response to all variables. Its performance compared to observations was the same as the original model. The computational cost of the full model is about 8 minutes on 16 cores (for a single time step), while the reduced/emulated model requires only 50 ms on one core <ref xlink:href="#clime-2013-bid10" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
      </subsection>
      <subsection id="uid66" level="2">
        <bodyTitle>Motion estimation from images with a waveforms reduced model</bodyTitle>
        <participants>
          <person key="clime-2005-id18242">
            <firstname>Etienne</firstname>
            <lastname>Huot</lastname>
          </person>
          <person key="clime-2005-id18081">
            <firstname>Isabelle</firstname>
            <lastname>Herlin</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Giuseppe</firstname>
            <lastname>Papari</lastname>
            <moreinfo>Lithicon, Norway</moreinfo>
          </person>
          <person key="clime-2009-id59717">
            <firstname>Karim</firstname>
            <lastname>Drifi</lastname>
          </person>
        </participants>
        <p>Dimension reduction is applied to an image model, composed of Lagrangian
constancy of velocity and transport of image brightness. Waveforms basis are
obtained on the image domain for subspaces of images, motion fields
and divergence-free motion fields, as eigenvectors of quadratic functions. Image assimilation with th reduced model
allows to estimate velocity fields satisfying space-time properties defined by
user and traduced as a quadratic function. This approach also solves the issue of complex geographical domains and the
difficulty of applying boundary conditions on these domains. Results are
obtained with a reduced dimension of motion to a few scalars, to be compared
with the original problem that has the size of image domain <ref xlink:href="#clime-2013-bid11" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, <ref xlink:href="#clime-2013-bid12" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, <ref xlink:href="#clime-2013-bid13" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
      </subsection>
    </subsection>
    <subsection id="uid67" level="1">
      <bodyTitle>Ensemble forecasting with sequential aggregation</bodyTitle>
      <p>The aggregation of an ensemble of forecasts is an approach where the members
of an ensemble are given a weight before every forecast time, and where the
corresponding weighted linear combination of the forecasts provides an
improved forecast. A robust aggregation can be carried out so as to guarantee
that the aggregated forecast performs better, in the long run, than any linear
combination of the ensemble members with time-independent weights. The
approaches are then based on machine learning. The aggregation algorithms can
be applied to forecast analyses (generated from a data assimilation system),
so that the aggregated forecasts are naturally multivariate fields.</p>
      <subsection id="uid68" level="2">
        <bodyTitle>Application of sequential aggregation to meteorology</bodyTitle>
        <participants>
          <person key="clime-2013-idp140610148035024">
            <firstname>Paul</firstname>
            <lastname>Baudin</lastname>
          </person>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Gilles</firstname>
            <lastname>Stoltz</lastname>
            <moreinfo>CNRS</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Laurent</firstname>
            <lastname>Descamps</lastname>
            <moreinfo>Météo France</moreinfo>
          </person>
        </participants>
        <p>Nowadays, it is standard procedure to generate an ensemble of simulations for a meteorological forecast. Usually, meteorological centers produce a single forecast, out of the ensemble forecasts, computing the ensemble mean (where every model receives an equal weight). It is however possible to apply aggregation methods. When new observations are available, the meteorological centers also compute analyses. Therefore, we can apply the ensemble forecast of analyses. Ensembles of forecasts for wind velocity and mean sea level pressure, from Météo France, were aggregated. Preliminary results show significant improvements for mean sea level pressure.</p>
      </subsection>
      <subsection id="uid69" level="2">
        <bodyTitle>Sequential aggregation with uncertainty estimation</bodyTitle>
        <participants>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="clime-2010-id59613">
            <firstname>Sergiy</firstname>
            <lastname>Zhuk</lastname>
            <moreinfo>IBM research, Ireland</moreinfo>
          </person>
          <person key="clime-2013-idp140610148035024">
            <firstname>Paul</firstname>
            <lastname>Baudin</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Gilles</firstname>
            <lastname>Stoltz</lastname>
            <moreinfo>CNRS</moreinfo>
          </person>
        </participants>
        <p>An important issue is the estimation of the uncertainties associated with the aggregated forecasts. One investigated direction relies on the framework of machine learning, with the aggregation of an ensemble of probability density functions instead of the point forecasts of the ensemble.</p>
        <p>Another direction is to reformulate the aggregation problem in a filtering problem for the weights. The weights are supposed to satisfy some dynamics with unknown model error, which defines the state equation of a filter. An observation equation compares the aggregated forecast with the observations (or analyses) with known observational error variance. The filter finally computes estimates for the weights and quantifies their uncertainties. We applied a Kalman filter and a minimax filter for air quality forecasting. We also introduced a criterion that the filter results should satisfy if they are representative of the uncertainties <ref xlink:href="#clime-2013-bid14" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
      </subsection>
    </subsection>
    <subsection id="uid70" level="1">
      <bodyTitle>Uncertainty quantification</bodyTitle>
      <p>Many uncertainties limit the forecast skills of geophysical simulations: limited understanding of physical phenomena, simplified representation of a system state and of the physical processes, inaccurate data and approximate numerical solutions. In many applications, a deterministic forecast or analysis is not enough a result since its uncertainties may be very large. It is of high interest to evaluate the quality of a forecast, before observations are available, and the quality of an analysis at any location, observed or not. An even more desirable result is the full probability density of system state, which can only be derived from a fully stochastic approach.</p>
      <subsection id="uid71" level="2">
        <bodyTitle>Sensitivity analysis in the dispersion of radionuclides</bodyTitle>
        <participants>
          <person key="clime-2013-idp140610148048848">
            <firstname>Sylvain</firstname>
            <lastname>Girard</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Irène</firstname>
            <lastname>Korsakissok</lastname>
            <moreinfo>IRSN</moreinfo>
          </person>
        </participants>
        <p>We carried out a sensitivity analysis of the dispersion of radionuclides during Fukushima disaster. We considered the dispersion at regional scale, with the Eulerian transport model Polair3D from Polyphemus. The sensitivities to most input parameters were computed using the Morris method (with 8 levels and 100 trajectories). The influences of 19 scalar parameters were quantified. The scalar parameters were additive terms or multiplicative factors applied to 1D, 2D or 3D fields such as emission rates, precipitations, cloud height, wind velocity. It was shown that, depending on the output quantities of interest (various aggregated atmospheric and ground dose rates), the sensitivity to the inputs may greatly vary. Very few parameters show low sensitivity in any case. The vertical diffusion coefficient, the scavenging factors, the winds and precipitation intensity were found to be the most influential inputs. Most input variables related to the source term (emission rates, emission dates) also had a strong influence.</p>
      </subsection>
    </subsection>
    <subsection id="uid72" level="1">
      <bodyTitle>Image assimilation</bodyTitle>
      <p>Sequences of images, such as satellite acquisitions, display structures evolving in time. This information is recognized of major interest by
forecasters (meteorologists, oceanographers, etc.) in order to improve the information provided by numerical models.
However, these satellite images are mostly assimilated in
geophysical models on a point-wise basis, discarding the space-time
coherence visualized by the evolution of structures such as
clouds. Assimilating in an optimal way image data is of major interest and this issue should be considered in two
ways:</p>
      <simplelist>
        <li id="uid73">
          <p noindent="true">from the model's viewpoint, the location of
structures on the observations is used to control the state vector.</p>
        </li>
        <li id="uid74">
          <p noindent="true">from the image's viewpoint, a model of the dynamics and structures is
built from the observations.</p>
        </li>
      </simplelist>
      <subsection id="uid75" level="2">
        <bodyTitle>Divergence-free motion estimation</bodyTitle>
        <participants>
          <person key="clime-2005-id18214">
            <firstname>Dominique</firstname>
            <lastname>Béréziat</lastname>
            <moreinfo>UPMC</moreinfo>
          </person>
          <person key="clime-2005-id18081">
            <firstname>Isabelle</firstname>
            <lastname>Herlin</lastname>
          </person>
          <person key="clime-2010-id59613">
            <firstname>Sergiy</firstname>
            <lastname>Zhuk</lastname>
            <moreinfo>IBM Research, Ireland</moreinfo>
          </person>
        </participants>
        <p>This research addresses the issue of divergence-free motion estimation on an image sequence, acquired over a given temporal window. Unlike most state-of-the-art technics, which constrain the divergence to be
small thanks to Tikhonov regularization terms, a method that imposes a null value of divergence of the estimated motion is defined.</p>
        <p>Motion is either characterized by its vorticity value or by its coefficients
on a divergence-free basis and assumed to satisfy the Lagragian constancy
hypothesis. An image assimilation method, based on the 4D-Var technic, is
defined that estimates motion as a compromise between the evolution equations
of vorticity or projection coefficients and the observed sequence of images.</p>
        <p>The method is applied on
Sea Surface Temperature (SST) images acquired over Black Sea by NOAA-AVHRR sensors. The divergence-free assumption is roughly valid on these acquisitions, due to the small values of vertical velocity at the surface.</p>
      </subsection>
      <subsection id="uid76" level="2">
        <bodyTitle>Model error and motion estimation</bodyTitle>
        <participants>
          <person key="clime-2005-id18214">
            <firstname>Dominique</firstname>
            <lastname>Béréziat</lastname>
            <moreinfo>UPMC</moreinfo>
          </person>
          <person key="clime-2005-id18081">
            <firstname>Isabelle</firstname>
            <lastname>Herlin</lastname>
          </person>
        </participants>
        <p>Data assimilation technics are used to retrieve motion
from image sequences. These methods require a model of the underlying
dynamics, displayed by the evolution of image data. In order to quantify the
approximation linked to the chosen dynamic model, an error term is included in
the evolution equation of motion and a weak formulation of 4D-Var data
assimilation is designed. The cost function to be minimized simultaneously
depends on the initial motion field, at the begining of the studied temporal window, and on the error value at each time step. The result allows to assess the model error and analyze its impact on motion estimation.</p>
        <p>The approach has been used to estimate the impact of geophysical forces
(gravity, Coriolis, diffusion) and better assess the surface dynamics <ref xlink:href="#clime-2013-bid15" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
      </subsection>
      <subsection id="uid77" level="2">
        <bodyTitle>Tracking of structures from an image sequence</bodyTitle>
        <participants>
          <person key="clime-2012-idp140574056062016">
            <firstname>Yann</firstname>
            <lastname>Lepoittevin</lastname>
          </person>
          <person key="clime-2005-id18081">
            <firstname>Isabelle</firstname>
            <lastname>Herlin</lastname>
          </person>
          <person key="clime-2005-id18214">
            <firstname>Dominique</firstname>
            <lastname>Béréziat</lastname>
            <moreinfo>UPMC</moreinfo>
          </person>
        </participants>
        <p>The research concerns an approach to estimate velocity on an image sequence
and simultaneously segment and track a given structure. It relies on the
underlying dynamics' equations of the studied physical system. A data
assimilation method is designed to solve evolution equations of image
brightness, those of motion's dynamics, and those of the distance map modeling
the tracked structures. The method is applied on meteorological satellite
data, in order to track tropical clouds on image sequences and estimate their
motion, as seen on Fig. <ref xlink:href="#uid78" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
        <object id="uid78">
          <table rend="inline">
            <tr style="">
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/tracking-3.png" type="inline" width="68.28644pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/tracking-9.png" type="inline" width="68.28644pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/tracking-18.png" type="inline" width="68.28644pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
            </tr>
            <caption/>
          </table>
          <caption>Tracking a tropical cloud. Frames 3, 9, 18 of the sequence.</caption>
        </object>
        <p>Quantification is obtained on synthetic experiments by comparing
trajectories of characteristic points. The respective position of these points
on the last image of the sequence for different methods may be compared to
that obtained with ground truth as seen on Fig. <ref xlink:href="#uid82" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>.</p>
        <object id="uid82">
          <table rend="inline">
            <tr style="">
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/ComPts-17-ell.png" type="inline" scale="0.22" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
            </tr>
            <caption/>
          </table>
          <caption>Red point: ground truth. Blue point: our method. Green
point: Sun's optical flow. Blue
ellipse: our method is the best. Green ellipse: Sun's result
is the best. Grey ellipse : results are equivalent.</caption>
        </object>
        <p>Data assimilation is performed either with a 4D-Var variational
approach <ref xlink:href="#clime-2013-bid16" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, <ref xlink:href="#clime-2013-bid17" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, <ref xlink:href="#clime-2013-bid18" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>
or with an ensemble approach. In the last case, computation of the ensemble from
optical flow methods of the literature is currently studied.
</p>
      </subsection>
    </subsection>
    <subsection id="uid83" level="1">
      <bodyTitle>Minimax filtering</bodyTitle>
      <p>In minimax filtering for state estimation, the initial state error, the model
error and the observation errors are supposed to belong to one
joint ellipsoid. It is only assumed that the errors, stochastic
or deterministic, are bounded. During the assimilation process, the filter
computes an ellipsoid where one will find at least all states compatible with
observations and errors description. The state estimate is taken as the center
of the ellipsoid. No assumption on the actual distribution of the errors in
needed and the state estimate minimizes the worst-case error, which makes the
filter robust.</p>
      <subsection id="uid84" level="2">
        <bodyTitle>Retrieval of a continuous image function and a posteriori minimax motion estimation </bodyTitle>
        <participants>
          <person key="clime-2010-id59613">
            <firstname>Sergiy</firstname>
            <lastname>Zhuk</lastname>
            <moreinfo>IBM Research, Ireland</moreinfo>
          </person>
          <person key="clime-2005-id18081">
            <firstname>Isabelle</firstname>
            <lastname>Herlin</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Olexander</firstname>
            <lastname>Nakonechnyi</lastname>
            <moreinfo>Taras Shevchenko National University of Kyiv</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Jason</firstname>
            <lastname>Frank</lastname>
            <moreinfo>CWI, the Netherlands</moreinfo>
          </person>
        </participants>
        <p>An iterative minimax method is developed for the problem of motion estimation
from an image sequence. The main idea of the
algorithm is to use the "bi-linear" structure of the Navier-Stokes
equations and optical flow constraint in order to iteratively estimate
the velocity. The algorithm consists of the following parts:</p>
        <p>1) we construct a continuous image function <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mover accent="true"><mi>I</mi><mo>^</mo></mover></math></formula>, solving the optical flow
constraint, such that <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mover accent="true"><mi>I</mi><mo>^</mo></mover></math></formula> fits (in the sense of least-squares) the
observed sequence of images. To do so, we set the velocity field in the
optical flow constraint to be the current minimax estimate of the
velocity field <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mi>𝐰</mi></math></formula>, obtained at the previous iteration of the
algorithm, and construct the minimax estimate <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mover accent="true"><mi>I</mi><mo>^</mo></mover></math></formula>
of the resulting linear advection equation using the observed image sequence as
discrete measurements of the brightness function;</p>
        <p>2) we plug the estimate of the image gradient, obtained out of
pseudo-observations <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mover accent="true"><mi>I</mi><mo>^</mo></mover></math></formula> in 1), into the optical flow constraint
and the current minimax estimate <formula type="inline"><math xmlns="http://www.w3.org/1998/Math/MathML" overflow="scroll"><mi>𝐰</mi></math></formula> of the velocity field into the non
linear part of Navier-Stokes equations so that we end up with a system of linear PDEs,
which represents an extended state equation: it contains a linear
parabolic equation for the velocity field and linear advection
equation for the image brightness function. We construct the minimax
estimate of the velocity field from the extended state equation using again the
observed image sequence as
discrete measurements of the brightness function;</p>
        <p>3) we use the minimax estimate of the velocity field obtained in 2) in
order to start 1) again.</p>
        <p>Alternatively, point 1) may be used to retrieve a continuous image function
from sparse and noisy image snapshots, based on previous motion estimation
with a 4D-Var technic as seen on Fig. <ref xlink:href="#uid85" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>, that displays
ground truth, noisy image observation, image estimation at the end of the
studied intervall.</p>
        <object id="uid85">
          <table rend="inline">
            <tr style="">
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/I8001-crop.png" type="inline" width="113.81102pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/Y8001-crop.png" type="inline" width="113.81102pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td style="text-align:center;" halign="center">
                <ressource xlink:href="IMG/mE8001-crop.png" type="inline" width="113.81102pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
            </tr>
            <caption/>
          </table>
          <caption>From left to right: Ground truth, image observation, result.</caption>
        </object>
      </subsection>
    </subsection>
    <subsection id="uid89" level="1">
      <bodyTitle>Fire application</bodyTitle>
      <subsection id="uid90" level="2">
        <bodyTitle>Model evaluation for fire propagation</bodyTitle>
        <participants>
          <person key="clime-2005-id18368">
            <firstname>Vivien</firstname>
            <lastname>Mallet</lastname>
          </person>
          <person key="PASUSERID">
            <firstname>Jean-Baptiste</firstname>
            <lastname>Fillipi</lastname>
            <moreinfo>CNRS</moreinfo>
          </person>
          <person key="PASUSERID">
            <firstname>Bahaa</firstname>
            <lastname>Nader</lastname>
            <moreinfo>University of Corsica</moreinfo>
          </person>
        </participants>
        <p>In the field of forest fires risk management, important challenges exist in
terms of people and goods preservation. Answering to strong needs from
different actors (firefighters, foresters), researchers focus their efforts to
develop operational decision support system tools that may forecast wildfire
behavior. This requires the evaluation of model performance, but currently,
simulation errors are not sufficiently qualified and quantified.</p>
        <p>We consider that the proper evaluation of a model requires to
apply it to a large number of fires – instead of carrying out a fine tuning
on just one fire. We implemented a software to simulate a large number of
fires (from the Prométhée database, <ref xlink:href="http://www.promethee.com/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>promethee.<allowbreak/>com/</ref>) with
the simulation model ForeFire (CNRS/University of Corsica) and evaluate the
results with error measures <ref xlink:href="#clime-2013-bid19" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>. One simulation requires mainly the following
data: the ignition point, the ground elevation, the vegetation cover and the
wind field. See illustration in Fig. <ref xlink:href="#uid91" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>. We simulated 80 fires with four physical models, which proved that the most advanced models performed better overall, even though the input data is often inaccurate. We also carried out Monte Carlo simulations to evaluate the impact of the uncertainty in input data. We showed that the Monte Carlo approach led to a reliable forecasting system, which suggests that the probability densities derived from the simulations (see Fig. <ref xlink:href="#uid91" location="intern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>) may be useful information for preventive actions in an operational context.</p>
        <object id="uid91">
          <table>
            <tr>
              <td>
                <ressource xlink:href="IMG/San-Giovanni-di-Moriani_04-08-2003.jpg" type="inline" width="125.19194pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
              <td>
                <ressource xlink:href="IMG/probability-non_stat-0-Patrimonio_11-02-2005.png" type="inline" width="125.19194pt" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest" media="WEB"/>
              </td>
            </tr>
          </table>
          <caption>Left: Fire simulation (using ForeFire) in red elevated contour, and
observation (from Prométhée) of the burned area in filled red contour, for
a 2003 fire near San-Giovanni-di-Moriani (Corsica). Right: Burn probability as computed by a Monte Carlo simulation for a wildfire that was observed (red contour) in Corsica in 2003.</caption>
        </object>
      </subsection>
    </subsection>
  </resultats>
  <contrats id="uid92">
    <bodyTitle>Bilateral Contracts and Grants with Industry</bodyTitle>
    <subsection id="uid93" level="1">
      <bodyTitle>Bilateral Contracts with Industry</bodyTitle>
      <simplelist>
        <li id="uid94">
          <p noindent="true">Clime is partner with INERIS (National Institute for Environmental and
Industrial Risks <ref xlink:href="http://www.ineris.com/en" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>ineris.<allowbreak/>com/<allowbreak/>en</ref>) in a joint cooperation devoted to air quality forecast. This
includes research topics in uncertainty estimation, data assimilation and
ensemble modeling.</p>
          <p>Clime also provides support to INERIS in order to operate the Polyphemus
system for ensemble forecasting, uncertainty estimations and operational data assimilation at continental scale.</p>
        </li>
        <li id="uid95">
          <p noindent="true">Clime is partner with IRSN <ref xlink:href="http://www.irsn.fr/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>irsn.<allowbreak/>fr/</ref>, the French national institute for radioprotection
and nuclear safety, for inverse modeling of emission sources and uncertainty
estimation of dispersion simulations. The collaboration aims at better
estimating emission sources, at improving operational forecasts for crisis
situations and at estimating the reliability of forecasts. The work is
derived at large scale (continental scale) and small scale (a few kilometers
around a nuclear power plant).</p>
        </li>
        <li id="uid96">
          <p noindent="true">Clime takes part to a joint Ilab with the group SETH (Numtech <ref xlink:href="http://www.numtech.fr/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>numtech.<allowbreak/>fr/</ref>). The objective
is to (1) transfer Clime work in data assimilation, ensemble forecasting and
uncertainty estimation, with application to urban air quality, (2) identify
the specific problems encountered at urban scale in order to determine new
research directions.</p>
        </li>
      </simplelist>
    </subsection>
  </contrats>
  <partenariat id="uid97">
    <bodyTitle>Partnerships and Cooperations</bodyTitle>
    <subsection id="uid98" level="1">
      <bodyTitle>National Initiatives</bodyTitle>
      <subsection id="uid99" level="2">
        <bodyTitle>ANR</bodyTitle>
        <simplelist>
          <li id="uid100">
            <p noindent="true">The ANR project Estimair aims at quantifying the uncertainties of air quality simulations at urban scale. The propagation of uncertainties requires the use of model reduction and emulation. A key uncertainty source lies in the traffic emissions, which will be generated using a dynamic trafic assignment model. Ensembles of traffic assignments will be calibrated and used in the uncertainty quantification. Estimair is led by Clime.</p>
          </li>
          <li id="uid101">
            <p noindent="true">Clime is one partner of the ANR project GeoFluids. It focuses on
the specification of tools to analyse geophysical fluid flows from image
sequences. Clime objectives concern the definition of reduced models from
image data.</p>
          </li>
          <li id="uid102">
            <p noindent="true">Clime takes part to the ANR project IDEA that addresses the propagation
of wildland fires. Clime is in charge of the estimation of the
uncertainties, based on sensitivity studies and ensemble simulations.</p>
          </li>
        </simplelist>
      </subsection>
      <subsection id="uid103" level="2">
        <bodyTitle>PRIMEQUAL (ADEME)</bodyTitle>
        <simplelist>
          <li id="uid104">
            <p noindent="true">Clime takes part to the PRIMEQUAL project PREQUALIF, “Programme Pluridisciplinaire de REcherche sur la QUALité de l'air en Île-de-France” (i.e., “Multidisciplinary Program on Air quality research in Île-de-France”). The objective is to investigate the impact of low emission zones. The project aims at designing a new generation of diagnostic tools for assessment of health and analysis of economic benefits attributed to traffic restrictions. Clime brings data assimilation expertise which allows to compute the most accurate air pollution maps.</p>
          </li>
        </simplelist>
      </subsection>
    </subsection>
    <subsection id="uid105" level="1">
      <bodyTitle>European Initiatives</bodyTitle>
      <subsection id="uid106" level="2">
        <bodyTitle>Collaborations in European Programs, except FP7</bodyTitle>
        <sanspuceslist>
          <li id="uid107">
            <p noindent="true">Program: COST Action ES104.</p>
          </li>
          <li id="uid108">
            <p noindent="true">Project acronym: EuMetChem.</p>
          </li>
          <li id="uid109">
            <p noindent="true">Project title: European framework for online integrated air
quality and meteorology modeling.</p>
          </li>
          <li id="uid110">
            <p noindent="true">Duration: January 2011 - December 2014.</p>
          </li>
          <li id="uid111">
            <p noindent="true">Coordinator: Alexander Baklanov, Danish Meteorological
Institute (DMI) Danemark.</p>
          </li>
          <li id="uid112">
            <p noindent="true">Other partners: around 14 european laboratories, experts from
United States, ECMWF.</p>
          </li>
          <li id="uid113">
            <p noindent="true">Abstract: European framework for online integrated air
quality and meteorology modeling (EuMetChem) focuses on
a new generation of online integrated Atmospheric Chemical
Transport (ACT) and Meteorology (Numerical Weather
Prediction and Climate) modeling with two-way interactions
between different atmospheric processes including chemistry
(both gases and aerosols), clouds, radiation, boundary
layer, emissions, meteorology and climate. Two
application areas of the integrated modeling are
considered: (i) improved numerical weather prediction
(NWP) and chemical weather forecasting (CWF) with
short-term feedbacks of aerosols and chemistry on
meteorological variables, and (ii) two-way interactions
between atmospheric pollution/ composition and climate
variability/change. The framework consists of four
working groups namely: 1) Strategy and framework for online
integrated modeling; 2) Interactions, parameterizations and
feedback mechanisms; 3) Chemical data assimilation in
integrated models; and finally 4) Evaluation, validation,
and applications. Establishment of such a European
framework (involving also key American experts) enables
the EU to develop world class capabilities in integrated
ACT/NWP-Climate modeling systems, including research,
forecasting and education.</p>
          </li>
        </sanspuceslist>
      </subsection>
      <subsection id="uid114" level="2">
        <bodyTitle>Collaborations with Major European Organizations</bodyTitle>
        <sanspuceslist>
          <li id="uid115">
            <p noindent="true">Partner: ERCIM working group “Environmental Modeling”.</p>
          </li>
          <li id="uid116">
            <p noindent="true">The working group gathers laboratories working on developing
models, processing environmental data or data assimilation.</p>
          </li>
        </sanspuceslist>
      </subsection>
    </subsection>
    <subsection id="uid117" level="1">
      <bodyTitle>International Initiatives</bodyTitle>
      <subsection id="uid118" level="2">
        <bodyTitle>Inria International Partners</bodyTitle>
        <subsection id="uid119" level="3">
          <bodyTitle>Informal International Partners</bodyTitle>
          <sanspuceslist>
            <li id="uid120">
              <p noindent="true">Partner: Chilean meteorological office
(Dirección Meteorológica de Chile)</p>
            </li>
            <li id="uid121">
              <p noindent="true">The partner produces its operational air quality
forecasts with Polyphemus. The 3-day forecasts essentially cover
Santiago. The forecasts are accessible online in the form of maps, time
series and video
(<ref xlink:href="http://www.meteochile.gob.cl/modeloPOLYPHEMUS.php" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>www.<allowbreak/>meteochile.<allowbreak/>gob.<allowbreak/>cl/<allowbreak/>modeloPOLYPHEMUS.<allowbreak/>php</ref>).</p>
            </li>
          </sanspuceslist>
          <p>‎</p>
          <sanspuceslist>
            <li id="uid122">
              <p noindent="true">Partner: Marine Hydrophysical Institute <ref xlink:href="http://mhi.nas.gov.ua/eng/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>mhi.<allowbreak/>nas.<allowbreak/>gov.<allowbreak/>ua/<allowbreak/>eng/</ref>, Ukraine.</p>
            </li>
            <li id="uid123">
              <p noindent="true">The collaboration concerns the study of the Black Sea surface
circulation and the issue of image assimilation in forecasting models.</p>
            </li>
          </sanspuceslist>
          <sanspuceslist>
            <li id="uid124">
              <p noindent="true">Partner: IBM Research, Dublin, Ireland</p>
            </li>
            <li id="uid125">
              <p noindent="true">The collaboration addresses the assimilation of classical
observations as well as images, with application to geophysics. New assimilation methods are developed, mainly based on minimax filtering.</p>
            </li>
          </sanspuceslist>
        </subsection>
      </subsection>
    </subsection>
    <subsection id="uid126" level="1">
      <bodyTitle>International Research Visitors</bodyTitle>
      <subsection id="uid127" level="2">
        <bodyTitle>Visits of International Scientists</bodyTitle>
        <simplelist>
          <li id="uid128">
            <p noindent="true">Sergiy Zhuk, IBM, Dublin Research Lab, Ireland, September 2013.</p>
          </li>
        </simplelist>
      </subsection>
    </subsection>
  </partenariat>
  <diffusion id="uid129">
    <bodyTitle>Dissemination</bodyTitle>
    <subsection id="uid130" level="1">
      <bodyTitle>Scientific Animation</bodyTitle>
      <simplelist>
        <li id="uid131">
          <p noindent="true">Marc Bocquet is a member of the INSU/LEFE MANU scientific commitee.</p>
        </li>
        <li id="uid132">
          <p noindent="true">Marc Bocquet is a member of the Scientific Council of the CERFACS institute in Toulouse, France.</p>
        </li>
        <li id="uid133">
          <p noindent="true">Marc Bocquet is Associate Editor of the Quaterly Journal of the Royal Meteorological Society.</p>
        </li>
        <li id="uid134">
          <p noindent="true">Marc Bocquet co-organised the LEFE-MANU workshop “Que peuvent attendre les modélisateurs de l'assimilation de données ?” with Frédéric Chevallier and Jacques Verron,12 February 2013, Inria, Paris, France.</p>
        </li>
        <li id="uid135">
          <p noindent="true">Marc Bocquet co-organised the symposium “Open session on Data Assimilation” with Jacques Blum, and Olivier Talagrand. MCPIT 2013, GDRE ConEDP, Insitut Henri Poincaré, Paris, France, 19 November 2013.</p>
        </li>
        <li id="uid136">
          <p noindent="true">Isabelle Herlin is a member of the Scientific Council of CSFRS (High
Council for Strategic Education and Research in France).</p>
        </li>
        <li id="uid137">
          <p noindent="true">Isabelle Herlin is a member of the program committee of DIGITEO, french
research cluster in science and technology of information.</p>
        </li>
        <li id="uid138">
          <p noindent="true">Isabelle Herlin is a member of the Scientific Council of OSU-EFLUVE.</p>
        </li>
        <li id="uid139">
          <p noindent="true">Isabelle Herlin is a member of Evaluation Committee at Inria.</p>
        </li>
        <li id="uid140">
          <p noindent="true">Isabelle Herlin co-organised a session on operational oceanography in
the European Geosciences Union General Assembly 2013 (EGU2013), 07-12 April 2013,
Vienna, Austria.</p>
        </li>
        <li id="uid141">
          <p noindent="true">Isabelle Herlin is a member of the scientific committee of the
conference “Image Sequence Analysis for Object and Change Detection”,
organized by the International Society for Photogrammetry and Remote Sensing (ISPRS).</p>
        </li>
      </simplelist>
    </subsection>
    <subsection id="uid142" level="1">
      <bodyTitle>Teaching - Supervision - Juries</bodyTitle>
      <subsection id="uid143" level="2">
        <bodyTitle>Teaching</bodyTitle>
        <sanspuceslist>
          <li id="uid144">
            <p noindent="true">Master OACOS/WAPE: Marc Bocquet, Vivien Mallet; Introduction to Data Assimilation for Geophysics; 30 hours; M2; UPMC, X, ENS, ENSTA ParisTech, École des Ponts ParisTech; France.</p>
          </li>
          <li id="uid145">
            <p noindent="true">Master "Nuclear Energy": Marc Bocquet, Vivien Mallet;
12 hours; M2; École des Ponts ParisTech; France.</p>
          </li>
          <li id="uid146">
            <p noindent="true">Master SGE and École des Ponts ParisTech: Vivien Mallet; Air Pollution;
6 hours; M2; École des Ponts ParisTech , Paris 7-Diderot, Paris Est; France.</p>
          </li>
          <li id="uid147">
            <p noindent="true">Master in applied mathematics and scientific computing: Vivien Mallet; Introduction to Data Assimilation and Uncertainty Quantification in Geosciences;
11 hours; M2; Sup'Galilée, University Paris 13, École centrale Marseille; France.</p>
          </li>
          <li id="uid148">
            <p noindent="true">Training: Vivien Mallet; Uncertainty Quantification: Ensembles and Data Assimilation – Application to Climate and Geosciences;
5.25 hours; CERFACS; France.</p>
          </li>
        </sanspuceslist>
      </subsection>
      <subsection id="uid149" level="2">
        <bodyTitle>Supervision</bodyTitle>
        <sanspuceslist>
          <li id="uid150">
            <p noindent="true">PhD : Karim Drifi, “Reduced models for image assimilation”,
University Paris Centre, July 1st, 2012, Isabelle Herlin.</p>
          </li>
          <li id="uid151">
            <p noindent="true">PhD : Yiguo Wang, "Une nouvelle approche de modélisation de la qualité de l’air à l’échelle régionale par assimilation de mesures lidar", École Polytechnique, 20 December 2013, Marc Bocquet, Karine Sartelet, Patrick Chazette.</p>
          </li>
          <li id="uid152">
            <p noindent="true">PhD in progress : Paul Baudin, “Agrégation séquentielle de
prédicteurs appliquée à la prévision de la qualité de l'air”,
September 2012, Vivien Mallet and Gilles Stoltz.</p>
          </li>
          <li id="uid153">
            <p noindent="true">PhD in progress : Jean-Matthieu Haussaire, “Méthodes variationnelles d'ensemble
pour la modélisation inverse en géosciences. Application au transport et la chimie atmosphérique”,
University Paris-Est, October 2013, Marc Bocquet.</p>
          </li>
          <li id="uid154">
            <p noindent="true">PhD in progress : Yann Lepoittevin, “Tracking of image structures”,
University Paris Centre, October 2012, Isabelle Herlin.</p>
          </li>
          <li id="uid155">
            <p noindent="true">PhD in progress : Jean Thorey, “Prévision d'ensemble du rayonnement solaire pour la production photovoltaïque du parc EDF”,
November 2013, Vivien Mallet.</p>
          </li>
          <li id="uid156">
            <p noindent="true">PhD in progress : Victor Winiarek, “Dispersion atmosphérique en
milieu urbain et modélisation inverse pour la reconstruction de sources”,
University Paris Est, October 2009, Marc Bocquet.</p>
          </li>
        </sanspuceslist>
      </subsection>
      <subsection id="uid157" level="2">
        <bodyTitle>Juries</bodyTitle>
        <simplelist>
          <li id="uid158">
            <p noindent="true">Bocquet, M., member, PhD thesis, Benjamin Gaubert, “Assimilation des observations pour la modélisation de la qualité de l’air”, Paris Diderot University , 8 July 2013, Créteil, France.</p>
          </li>
          <li id="uid159">
            <p noindent="true">Bocquet, M., member, PhD thesis, Bertrand Bonan, “Assimilation de données pour l'initialisation et l'estimation de paramètres d'un modèle d'évolution de calotte polaire”, 15 November 2013, Grenoble University, Grenoble, France.</p>
          </li>
          <li id="uid160">
            <p noindent="true">Bocquet, M., member, PhD thesis, Yiguo Wang, “Une nouvelle approche de modélisation de la qualité de l'air à l'échelle régionale par assimilation de mesures lidar”, 20 December 2013, University Paris-Est, Champs-sur-Marne, France.</p>
          </li>
          <li id="uid161">
            <p noindent="true">Herlin, I., reviewer, PhD thesis, Anastase Charantonis, “Méthodologie d'inversion de
données océaniques de surface pour la reconstitution de profils verticaux en
utilisant des chaînes de Markov cachées et des cartes auto-organisatrices”,
January 24th 2013, Paris, France.</p>
          </li>
        </simplelist>
      </subsection>
    </subsection>
    <subsection id="uid162" level="1">
      <bodyTitle>Popularization</bodyTitle>
      <simplelist>
        <li id="uid163">
          <p noindent="true">Marc Bocquet made a presentation on employment in the environment
sector at the second “Forum Maths Emploi”, January 2013, Paris.</p>
        </li>
        <li id="uid164">
          <p noindent="true">Marc Bocquet wrote a paper <ref xlink:href="#clime-2013-bid20" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> on “Modélisation numérique de la
dispersion atmosphérique accidentelle des radionucléides : l'état de l'art
de la recherche” in the journal “Revue du
Centre de Défense NBC”.</p>
        </li>
        <li id="uid165">
          <p noindent="true">Isabelle Herlin and Vivien Mallet wrote an introduction to air quality
simulation <ref xlink:href="#clime-2013-bid21" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/> for a special issue on
Mathematics for Planet Earth dedicated to teachers in french “collèges”
and “lycées” and an internet contribution <ref xlink:href="#clime-2013-bid22" location="biblio" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest"/>
“Votre air, votre santé”: 
<ref xlink:href="http://mpt2013.fr/votre-air-votre-sante/" location="extern" xlink:type="simple" xlink:show="replace" xlink:actuate="onRequest">http://<allowbreak/>mpt2013.<allowbreak/>fr/<allowbreak/>votre-air-votre-sante/</ref></p>
        </li>
        <li id="uid166">
          <p noindent="true">Vivien Mallet introduced numerical simulation of air pollution at the 2013 edition of “Mathématiques en mouvement”.</p>
        </li>
        <li id="uid167">
          <p noindent="true">Vivien Mallet and Anne Tilloy took part to the festival “Futur en Seine” and presented, during four days, research advances in air quality simulation at urban scale.</p>
        </li>
      </simplelist>
    </subsection>
  </diffusion>
  <biblio id="bibliography" html="bibliography" numero="10" titre="Bibliography">
    
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        <title level="a">An iterative ensemble Kalman smoother</title>
        <author>
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            <foreName>Marc</foreName>
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          </persName>
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            <foreName>Pavel</foreName>
            <surname>Sakov</surname>
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        </author>
      </analytic>
      <monogr x-editorial-board="yes" x-international-audience="yes">
        <title level="j">Quarterly Journal of the Royal Meteorological Society</title>
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