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  <front>
    <journal-meta />
    <article-meta>
      <title-group>
        <article-title>LifeCLEF Plant Identi cation Task 2014</article-title>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <string-name>Herve Goeau</string-name>
          <xref ref-type="aff" rid="aff4">4</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Alexis Joly</string-name>
          <xref ref-type="aff" rid="aff4">4</xref>
          <xref ref-type="aff" rid="aff5">5</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Pierre Bonnet</string-name>
          <email>pierre.bonnet@cirad.fr</email>
          <xref ref-type="aff" rid="aff1">1</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Souheil Selmi</string-name>
          <xref ref-type="aff" rid="aff4">4</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Jean-Franois Molino</string-name>
          <email>wjean-francois.molino@ird.fr</email>
          <xref ref-type="aff" rid="aff3">3</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Daniel Barthelemy</string-name>
          <email>daniel.barthelemy@cirad.fr</email>
          <xref ref-type="aff" rid="aff0">0</xref>
        </contrib>
        <contrib contrib-type="author">
          <string-name>Nozha Boujemaa</string-name>
          <email>nozha.boujemaa@inria.fr</email>
          <xref ref-type="aff" rid="aff2">2</xref>
        </contrib>
        <aff id="aff0">
          <label>0</label>
          <institution>CIRAD, BIOS Direction and INRA, UMR AMAP</institution>
          ,
          <addr-line>F-34398</addr-line>
          ,
          <country country="FR">France</country>
        </aff>
        <aff id="aff1">
          <label>1</label>
          <institution>CIRAD, UMR AMAP</institution>
          ,
          <country country="FR">France</country>
        </aff>
        <aff id="aff2">
          <label>2</label>
          <institution>INRIA, Direction of Saclay Center</institution>
        </aff>
        <aff id="aff3">
          <label>3</label>
          <institution>IRD</institution>
          ,
          <addr-line>UMR AMAP</addr-line>
          ,
          <country country="FR">France</country>
        </aff>
        <aff id="aff4">
          <label>4</label>
          <institution>Inria ZENITH team</institution>
          ,
          <country country="FR">France</country>
        </aff>
        <aff id="aff5">
          <label>5</label>
          <institution>LIRMM</institution>
          ,
          <addr-line>Montpellier</addr-line>
          ,
          <country country="FR">France</country>
        </aff>
      </contrib-group>
      <fpage>598</fpage>
      <lpage>615</lpage>
      <abstract>
        <p>The LifeCLEFs plant identi cation task provides a testbed for a system-oriented evaluation of plant identi cation about 500 species trees and herbaceous plants. Seven types of image content are considered: scan and scan-like pictures of leaf, and 6 kinds of detailed views with unconstrained conditions, directly photographed on the plant: ower, fruit, stem &amp; bark, branch, leaf and entire view. The main originality of this data is that it was speci cally built through a citizen sciences initiative conducted by Tela Botanica, a French social network of amateur and expert botanists. This makes the task closer to the conditions of a realworld application. This overview presents more precisely the resources and assessments of task, summarizes the retrieval approaches employed by the participating groups, and provides an analysis of the main evaluation results. With a total of ten groups from six countries and with a total of twenty seven submitted runs, involving distinct and original methods, this fourth year task con rms Image &amp; Multimedia Retrieval community interest for biodiversity and botany, and highlights further challenging studies in plant identi cation.</p>
      </abstract>
      <kwd-group>
        <kwd>LifeCLEF</kwd>
        <kwd>plant</kwd>
        <kwd>leaves</kwd>
        <kwd>leaf</kwd>
        <kwd>ower</kwd>
        <kwd>fruit</kwd>
        <kwd>bark</kwd>
        <kwd>stem</kwd>
        <kwd>branch</kwd>
        <kwd>species</kwd>
        <kwd>retrieval</kwd>
        <kwd>images</kwd>
        <kwd>collection</kwd>
        <kwd>identi cation</kwd>
        <kwd>ne-grained classi cation</kwd>
        <kwd>evaluation</kwd>
        <kwd>benchmark</kwd>
      </kwd-group>
    </article-meta>
  </front>
  <body>
    <sec id="sec-1">
      <title>-</title>
      <p>
        Content-based image retrieval approaches are nowadays considered to be one
of the most promising solution to help bridge the botanical taxonomic gap, as
discussed in [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ] or [
        <xref ref-type="bibr" rid="ref22">22</xref>
        ] for instance. We therefore see an increasing interest in this
trans-disciplinary challenge in the multimedia community (e.g. in [
        <xref ref-type="bibr" rid="ref12">12</xref>
        ], [
        <xref ref-type="bibr" rid="ref5">5</xref>
        ], [
        <xref ref-type="bibr" rid="ref20">20</xref>
        ],
[
        <xref ref-type="bibr" rid="ref23">23</xref>
        ], [
        <xref ref-type="bibr" rid="ref14">14</xref>
        ], [
        <xref ref-type="bibr" rid="ref2">2</xref>
        ]). Beyond the raw identi cation performances achievable by
stateof-the-art computer vision algorithms, the visual search approach o ers much
more e cient and interactive ways of browsing large oras than standard eld
guides or online web catalogs. Smartphone applications relying on such
imagebased identi cation services are particularly promising for setting-up massive
ecological monitoring systems, involving hundreds of thousands of contributors
at a very low cost.
      </p>
      <p>
        Noticeable progress in this way was achieved by several project and apps like
LeafSnap7 [
        <xref ref-type="bibr" rid="ref22">22</xref>
        ], PlantNet8,9 [
        <xref ref-type="bibr" rid="ref16">16</xref>
        ]. But as promising as these applications are, their
performances are however still far from the requirements of a real-world
socialbased ecological surveillance scenario. Allowing the mass of citizens to produce
accurate plant observations requires to equip them with much more accurate
identi cation tools. Measuring and boosting the performances of content-based
identi cation tools is therefore crucial. This was precisely the goal of the
ImageCLEF10 plant identi cation task organized since 2011 in the context of the
worldwide evaluation forum CLEF11(see [
        <xref ref-type="bibr" rid="ref10">10</xref>
        ], [
        <xref ref-type="bibr" rid="ref11">11</xref>
        ] and [
        <xref ref-type="bibr" rid="ref17">17</xref>
        ] for more details).
      </p>
      <p>Contrary to previous evaluations reported in the literature, the key objective
was since the rst campaign to build a realistic task closer to real-world
conditions (di erent users, cameras, areas, periods of the year, individual plants,
etc.). This was initially achieved through a citizen science initiative initiated 4
years ago in the context of the Pl@ntNet project in order to boost the image
production of Tela Botanica social network. The evaluation data was enriched
each year with the new contributions and progressively diversi ed with other
input feeds (annotation and cleaning of older data, contributions made through
Pl@ntNet mobile applications). The plant task of LifeCLEF 2014 is directly in
the continuity of this e ort. Main novelties compared to the last years are the
following:
{ an explicit multi-image query scenario,
{ the supply of user ratings on image quality in the meta-data,
{ a new type of view called "Branch" additionally to the 6 previous ones,
{ and basically more species: 500 which is an important step towards covering
the entire ora of a given region.
2</p>
    </sec>
    <sec id="sec-2">
      <title>Dataset</title>
      <p>
        More precisely, PlantCLEF 2014 dataset is composed of 60,962 pictures
belonging to 19,504 observations of 500 species of trees, herbs and ferns living in a
European region centered around France. This data was collected by 1608
distinct contributors. Each picture belongs to one and only one of the 7 types of
view reported in the meta-data (entire plant, fruit, leaf, ower, stem, branch,
leaf scan) and is associated with a single plant observation identi er allowing to
link it with the other pictures of the same individual plant (observed the same
day by the same person). It is noticeable that most image-based identi cation
methods and evaluation data proposed in the past were so far based on leaf
7 http://leafsnap.com/
8 https://play.google.com/store/apps/details?id=org.plantnet&amp;hl=en
9 http://identify.plantnet-project.org/
10 http://www.imageclef.org/
11 http://www.clef-initiative.eu/
images (e.g. in [
        <xref ref-type="bibr" rid="ref22">22</xref>
        ], [
        <xref ref-type="bibr" rid="ref3">3</xref>
        ], [
        <xref ref-type="bibr" rid="ref5">5</xref>
        ] or in the more recent methods evaluated in [
        <xref ref-type="bibr" rid="ref11">11</xref>
        ]).
Only few of them were focused on ower's images as in [
        <xref ref-type="bibr" rid="ref25">25</xref>
        ] or [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ]. Leaves are far
from being the only discriminant visual key between species but, due to their
shape and size, they have the advantage to be easily observed, captured and
described. More diverse parts of the plants however have to be considered for
accurate identi cation.
      </p>
      <p>An originality of PlantCLEF dataset is that its social nature makes it closer
to the conditions of a real-world identi cation scenario: (i) images of the same
species are coming from distinct plants living in distinct areas (ii) pictures are
taken by di erent users that might not used the same protocol to acquire the
images (iii) pictures are taken at di erent periods in the year. Each image of the
dataset is associated with contextual meta-data (author, date, locality name,
plant id) and social data (user ratings on image quality, collaboratively validated
taxon names, vernacular names) provided in a structured xml le. The gps
geolocalization and the device settings are available only for some of the images.
Table 1 gives some examples of pictures with decreasing averaged users ratings
for the di erent types of views. Note that the users of the specialized social
network creating these ratings (Tela Botanica) are explicitly asked to rate the
images according to their plant identi cation ability and their accordance to the
pre-de ned acquisition protocol for each view type. This is not an aesthetic or
general interest judgement as in most social image sharing sites.</p>
      <p>To sum up each image is associated with the following meta-data:
{ ObservationId: the plant observation ID from which several pictures can
be associated
{ FileName
{ MediaId: id of the image
{ View Content: Branch or Entire or Flower or Fruit or Leaf or LeafScan or</p>
      <p>Stem
{ ClassId: the class number ID that must be used as ground-truth. It is a
numerical taxonomical number used by Tela Botanica
{ Species the species names (containing 3 parts: the Genus name, the Species
name, the author(s) who discovered or revised the name of the species)
{ Genus: the name of the Genus, one level above the Species in the
taxonomical hierarchy used by Tela Botanica
{ Family: the name of the Family, two levels above the Species in the
taxonomical hierarchy used by Tela Botanica
{ Date: (if available) the date when the plant was observed,
{ Vote: the (round up) average of the user ratings on image quality
{ Location: (if available) locality name, most of the time a town
{ Latitude &amp; Longitude: (if available) the GPS coordinates of the
observation in the EXIF metadata, or, if no GPS information were found in the
EXIF, the GPS coordinates of the locality where the plant was observed
(only for the towns of metropolitan France)
{ Author: name of the author of the picture,
{ YearInCLEF: ImageCLEF2011, ImageCLEF2012, ImageCLEF2013,
PlantCLEF2014 when the image was integrated in the benchmark
{ IndividualPlantId2013: the plant observation ID used last year during
the ImageCLEF2013 plant task,
{ ImageID2013: the image id.jpg used in 2013.
3</p>
    </sec>
    <sec id="sec-3">
      <title>Task Description</title>
      <p>The task was evaluated as a plant species retrieval task based on multi-image
plant observations queries. The goal was to retrieve the correct plant species
among the top results of a ranked list of species returned by the evaluated
system. Contrary to previous plant identi cation benchmarks, queries are not
de ned as single images but as plant observations, meaning a set of one to
several images depicting the same individual plant, observed by the same person,
the same day, with the same device. Each image of a query observation is
associated with a single view type (entire plant, branch, leaf, fruit, ower, stem or
leaf scan) and with contextual meta-data (data, location, author). Each
participating group was allowed to submit up to 4 runs built from di erent methods.
Any human assistance in the processing of the test queries has therefore to be
signaled in the submitted runs meta-data.</p>
      <p>In practice, the whole PlantCLEF dataset was split in two parts, one for
training (and/or indexing) and one for testing. All observations with pictures used
in the previous plant identi cation tasks were directly integrated in the training
dataset. Then for the new observations and pictures, in order to guarantee that
most of the time each species contained more images in the training dataset than
in the test dataset, we used a constrained random rule for putting with priority
observations with more distinct organs and views in the training dataset. The
test set was built by choosing 1/2 of the observations of each species with this
constrained random rule, whereas the remaining observations were kept in the
reference training set. Thus, 1/3 of the pictures are in the test dataset (see Table
1 for more detailed stats). The xml les containing the meta-data of the query
images were purged so as to erase the taxon names (the ground truth) and the
image quality ratings (that would not be available at query stage in a real-world
mobile application). Meta-data of the observations in the training set are kept
unaltered.</p>
      <p>The metric used to evaluate the submitted runs is a score related to the rank
of the correct species in the returned list. Each query observation is attributed
with a score between 0 and 1 re ecting equal to the inverse of the rank of
the correct species (equal to 1 if the correct species is the top-1 decreasing
quickly while the rank of the correct species increases). An average score is
then computed across all plant observation queries. A simple mean on all plant
observation test would however introduce some bias. Indeed, we remind that the
PlantCLEF dataset was built in a collaborative manner. So that few contributors
might have provided much more observations and pictures than many other
contributors who provided few. Since we want to evaluate the ability of a system
to provide the correct answers to all users, we rather measure the mean of the
average classi cation rate per author. Finally, our primary metric was de ned
as the following average classi cation score S:</p>
      <p>S =
1 XU 1 XPu su;p</p>
      <p>U u=1 Pu p=1
where U : number of users (who have at least one image in the test data), Pu:
number of individual plants observed by the u-th user, su;p: the score between 1
and 0 equals to the inverse of the rank of the correct species (for the p-th plant
observed by the u-th user).</p>
      <p>A secondary metric was used to evaluate complementary (but not
mandatory) runs providing species prediction at the image level. Each test image is
attributed with a score between 0 and 1: of 1 if the 1st returned species is correct
and decrease quickly while the rank of the correct species increases. An average
score is then be computed on all test images. Following the same motivations
expressed above, a simple mean on all test images would however introduce some
bias. Some authors sometimes provided many pictures of the same individual
plant (to enrich training data with less e orts). Since we want to evaluate the
ability of a system to provide the correct answer based on a single plant
observation, we also have to average the classi cation rate on each individual plant.
Finally, our secondary metric is de ned as the following average classi cation
score S:</p>
      <p>S =
1 XU 1 XPu 1 NXu;p su;p;n</p>
      <p>U u=1 Pu p=1 Nu;p n=1
where U is the number of users, Pu the number of individual plants observed by
the u-th user, Nu;p the number of pictures of the p-th plant observation of the
u-th user, su;p;n is the score between 1 and 0 equals to the inverse of the rank
of the correct species.
4</p>
    </sec>
    <sec id="sec-4">
      <title>Participants and methods</title>
      <p>74 research groups worldwide registered to the plant task (31 of them being
exclusively registered to the plant task). Among this large raw audience, 10
research groups did cross the nish line by submitting runs (from 1 to 4 depending
on the teams). 6 teams submitted 14 complementary runs on images.</p>
      <p>
        Participants were mainly academics, specialized in computer vision, machine
learning and multimedia information retrieval. We list below the participants
and give a brief overview of the techniques they used in their runs. We remind
here that LifeCLEF benchmark is a system-oriented evaluation and not a deep
or ne evaluation of the underlying algorithms. Readers interested by the
scienti c and technical details of any of these methods should refer to the LifeCLEF
2014 working notes of each participant (referenced below):
BME TMIT (3 runs), [
        <xref ref-type="bibr" rid="ref29">29</xref>
        ], Hungary. These participants used Gaussian
Mixture Model (GMM) based Fisher vector (FV) representation from a
denseSIFT features extraction. Principal Component Analysis (PCA) is rst used on
(1)
(2)
the SIFT vectors in order to reduce the dimension from 128 to 80. Then a Fisher
Vector representation based on a concise codebook of 256 visual words is used
for embedding the PCA-SIFT descriptors in a single high level representation
for each image. The chosen classi er was the C-Support Vector Classi cation
(C-SVC) algorithm with Radial Basis Function kernel. The two
hyperparameters (C from C-SVC and from RBF kernel) were optimized by a grid search
with two-dimensional grid. The algorithm was trained with the training image
set, and then validated on the validation set, while the hyperparameters were
di erent in each iteration. In order to obtain a nal species list for all test images
from a same observation, since the C-SVC classi er calculates continuous
reliability value for each class at each image, they used a combined classi er using a
weighted average of reliability values.
      </p>
      <p>
        FINKI (3 runs) [
        <xref ref-type="bibr" rid="ref7">7</xref>
        ], Macedonia. For the LeafScan category these participants
used the multiscale triangular shape descriptor [
        <xref ref-type="bibr" rid="ref24">24</xref>
        ]. For the other pictures,
opponent SIFT were extracted around 20 000 points of interest obtained using
Harris-Laplace detector. In addition, a rhomboid-shaped mask was applied to
the input image to minimize the e ect of the cluttered background and to reduce
the number of points as in [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ]. Then an approximate k-means (AKM) algorithm
is used for clustering these descriptors and for producing a large number of
visual words (approximately 200K). Then, they used for each test image a
Bagof-visual-Word representation and used a classical TF-IDF measure in order to
compute a training image list. Finally, in order to combine the result lists from
several test images belonging to a same plant observation, two fusion operators
as experimented: Min rank (run 2), a "Probability fusion" (run 3). The
combination of the two approaches (run 1) gave their best results. Then a 1-nn rule is
used at the end for producing a list of ranked species.
      </p>
      <p>
        I3S (2 runs) [
        <xref ref-type="bibr" rid="ref15">15</xref>
        ], France. These participants used a Bag-of-Word framework
starting from SIFT and Opponent Color SIFT features extracted from 1000
points localised with the SIFT detector. Several visual dictionaries were
constructed with a K-means clustering algorithms: K=4000 words for the LeafScan
category, K=2000 for the Leaf, and K=500 for the other types of views. Then,
3500 (7 image categories x 500 species) SVM binary classi ers were trained in
order to give for each test image a list of species with a decreasing normalized
score of con dence. Pictures from a same test plant observation are gathered
according to two rules: sum (Run 1) and max (Run 2) of con dence normalized
scores.
      </p>
      <p>
        IBM AU (4 runs) [
        <xref ref-type="bibr" rid="ref6">6</xref>
        ], Australia. These participants tested and combined
distinct approaches. Run1 uses a deep Convolutional Neural Network. Their
CNN has around 60 million parameters and is composed of 5 convolutional
layers, some of which are followed by max-pooling layers, and three fully-connected
layers with a nal softmax layer. They followed the pipeline in [
        <xref ref-type="bibr" rid="ref21">21</xref>
        ], but they
restricted the node number of the fully connection network to 2048 as this number
is far more enough to model the plant images. Run 2 used a Gaussian Mixture
Model based Fisher Kernel approach. First, they extracted dense SIFT and Color
Moments (CMs) in images and each local feature was reduced to a 64-dim after
using PCA. Then for each type of features, a GMM model with 512 components
is estimated for producing two Fisher Vector representations by image. Then,
they averaged the output from linear trained SVMs classi ers, one for each type
of features. In Run 3 &amp; 4 they combined the CNN and the FV approaches with
an empirical rule. Run 4 is like the run 3 but with a segmentation preprocessing
step on images in order to nd better regions on interest to analyse (only on
Flower, Fruit, Leaf, LeafScan and Stem).
      </p>
      <p>
        IV-Processing (1 run) [
        <xref ref-type="bibr" rid="ref8">8</xref>
        ], Tunisia. These participants embeded several
types of features (the outputs of the harris detector, a haar wavelet
decomposition, a RGB color histogram) into a single binary code after a Principal
Component Analysis step. Then the hamming distance is used in order to
compare images from the training dataset with image query.
      </p>
      <p>
        MIRACL (3 runs) [
        <xref ref-type="bibr" rid="ref19">19</xref>
        ], Tunisia. This team tested visual and textual
approaches. For the visual part they used a combination of standard global
descriptors: Color Layout Descriptor (CLD), Edge Orientation Histogram (EOH)
and a Scalable Color Descriptor (SCD). Then, they attempted to use the
contextual content in the associated XML documents for each image with textual
and structural representations.
      </p>
      <p>
        PlantNet (4 runs) [
        <xref ref-type="bibr" rid="ref13">13</xref>
        ], France. These participants used for all categories a
large scale matching approach, and some shape descriptors in the speci c case of
LeafScan (Directional Fragment Histogram and standard shape parameters). A
geometrically constrained multi-scale &amp; multi-orientation Harris-Laplace
detector is used in order detect around 100-150 points mostly located at the center of
the pictures. Then, they extracted numerous local features: SURF, Fourier2D,
rotation invariant Local Binary Patterns, Edge Orientation Histogram, weighted
RGB, weighted-LUV and HSV histograms. After preliminary evaluations, each
type of view had its own subsets of types of local features. These local features
are hashed, indexed and searched in separate index with the Random Maximum
Margin Hashing approach (one for each type of view and for each type of
feature). Then, a hierarchical late fusion scheme is applied in order to combine the
image response lists of the di erent modalities: rst from the di erent types of
local features, then from the multiple-images from a same category, and nally
from all the categories in order to obtain a nal list related to one plant
observation. Di erent fusion algorithms are experimented in order to combine the
information at each level: a weighted probabilities approach (run 1), and the
BordaMNZ count (run 2,3,4) and IprMNZ count (run 4 only for LeafScan and
Fruit) inspired from the voting theory. The nal species list is produced thanks
to an adaptive k-nn rule (k being related to plant observations, not images).
QUT (1 run) [
        <xref ref-type="bibr" rid="ref28">28</xref>
        ], Australia. These participants used (Overfeat ) a
Convolutional Neural Network pre-trained with the generic ImageNet dataset previously
used to perform general object classi cation. They used two layers in this
network in order to obtain two sets of visual features: the Layer 17 gave a set of
3072-dim vectors, and Layer 19 gave a set of 4096-dim vectors. Then, a extremely
Randomized Trees Classi er is used in order to output a probability
distribution over the 500 species, one for each feature. The probability distributions are
then averaged in order to compute a single probability distribution for a test
image. Finally, probability distributions from several pictures from a same test
observation are added in order to obtain the nal list of ranked species. Note
that this kind of approach was not really allowed since the Overfeat features are
pre-trained with some external resources.
      </p>
      <p>
        Sabanki-Okan (2 runs) [
        <xref ref-type="bibr" rid="ref30">30</xref>
        ], Turkey. These participants used distinct
approaches, depending to the category of picture. For the LeafScan category, an
automatic segmentation was performed using edge preserving morphological
simpli cation by means of area attribute lters, followed by an adaptive threshold.
Then, a variety of shape and texture features are extracted (the same than the
ones used during the previous 2012-13 campaigns): Circular Covariance Hist.
(CCH), Rotation Invariant Point Triplets (RIT), Orientation Hist. (OH), Color
Auto-correlogram, etc. For the Flower, Fruit and Entire categories, they used a
Bag of Visual Word approach: they extracted some dense-SIFT features and used
a K-Means in order to obtain the visual dictionary of 1200 words and produce
BoW representations for each image. For the Stem category, they used the same
global descriptors on texture and color used for the LeafScan category (CCH,
OH, RIT) with an additional Morphological Covariance descriptor. Finally in
each system they used SVM classi ers for predicting a list of ranked species. In
the speci c case of Branch and Leaf categories, they used a Convolutional
Neural Network approach. The CNN employed contains 8 layers where the output
of the last fully connected softmax layer produces a distribution over the species.
SZTE (4 runs) [
        <xref ref-type="bibr" rid="ref26">26</xref>
        ], Hungary. The SZTE focused their work on the
LeafScan category: after a rst Otsu segmentation, they extracted a Vein
density description, various shape parameters (area/perimeter, perimeter/diameter,
diameter/perpendicular-diameter) and the cumulative histogram representation
of Multiscale Triangular shape descriptors successfully evaluated in last year
plant identi cation task [
        <xref ref-type="bibr" rid="ref18">18</xref>
        ], [
        <xref ref-type="bibr" rid="ref24">24</xref>
        ]. Then a Random Forest classi er is used for
predicting species. For the other categories, they used a Color-Gradient
Histogram CGH on pictures. The test images are then compared with the training
images and k-nn classi er gave a ranked species list. Finally an heuristic rule is
proposed for combining pictures from a same test plant observation by allowing
a priority to the LeafScan images.
      </p>
      <p>Table 2 attempts to summarize the methods used at di erent stages (feature,
classi cation,...) in order to highlight the main choices of participants.
5</p>
    </sec>
    <sec id="sec-5">
      <title>Results</title>
      <p>Main task
The following graphic 2 and table 3 show the scores obtained on the main task
on plant observation queries.</p>
      <p>
        The best results are indisputably obtained by the three last runs of the IBM
AU team. This results con rms that the Fisher Vector encoding is currently the
state-of-art as a generic approach in most of the problems in computer vision.
Convolutional Neural Networks, which is an another well-know recent
state-ofart technique for object recognition, have not performed as well here in this
problem of plant identi cation as we can see in the rst run of IBM AU or
the Sabanki-Okan runs. The main reason, as discussed in the working note of
IBM AU team [
        <xref ref-type="bibr" rid="ref6">6</xref>
        ], is that deep models usually require much training data to
learn their millions of parameters and avoid over tting (e.g. up to 1000 images
per class within ImagNet). To solve this issue, deep neural networks are usually
pre-trained on generalist classi cation tasks before being ne-tuned on the
targeted task. But as using external training data was not authorized in PlantCLEF
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2014, this approach could not be evaluated by the participants. Allowing such
approaches in next campaigns might be possible but is a tricky problem as we
need to guaranty that none of the images of test set could be found somewhere
on the web.</p>
      <p>Despite the supremacy of IBM sher vectors runs, it is surprising to see that
the performances of BME TMIT runs, which are based on a very close
training model, reached much lower performances. It demonstrates that di erent
implementations and parameters tuning can bring very di erent performances
(e.g. 512x60 sher vectors dimensions for IBM AU vs. 258x80 for BME TMIT,
IBM AU used additionnal Color Moments descriptors while BME TMIT used
only SIFT).Morever, like it was demonstrated during previous ImageCLEF Plant
Identi cation Task campaigns, teams who split the training data according to
the observation id during their preliminary evaluations on validation sets, seem
have to take bene t of it, avoiding certainly over tting problems like for the
IBM AU, PlantNet teams for instance. BME TMIT did not mentioned that and
may be were in this case, explaining also the di erence of performances with the
IBM AU runs.</p>
      <p>
        Another outcome is that the second best performing method from PlantNet
was already among the best performing methods in previous plant identi cation
challenges [
        <xref ref-type="bibr" rid="ref4">4</xref>
        ] although LifeCLEF dataset is much bigger and somehow more
complex because of the social dimension of the data. This demonstrates the
genericity and stability of the underlying matching method and features.
      </p>
      <p>This year few teams attempted to explore the metadata. The date was
exploited in the Sabanki-Okan runs, only on owers or fruits, but we don't have a
point of comparison in order to see if the use of this information was useful or not.
Miracl team attempted to combine the whole textual and structural informations
contained in the xml les, but it has been showed to degrade the performances
of their pure visual approach. Note that for the rst year, after three years of
unsuccessful attempts during the previous ImageCLEF Plant Identi cation Tasks,
none of the teams explored the locality and GPS information.
5.2</p>
      <p>Complementary results on images
6 teams submitted 14 complementary runs on images. The following graphic
3 and table 4 below present the scores obtained on the complementary run
les focusing on images. Thanks to the participants who produced these not
mandatory run les. In order to evaluate the bene t of the combination of the
test images from the same observation, the graphic compares the pairs of run
les on images and on observations assumed to have been produced with the
same method (it is not the case for the BME TMIT team). Basically, for each
method, we can observe a substantial improvement by combining the di erent
views from a same plant observation. It is a good news, since this is the current
practice of botanists, who most of the time can't identify a species with only one
picture on only one organ. However, we can say that the improvement are not
so much high: we guess that there is a room of improvement here, basically with
more images and may be with new methods of fusions dealing with this speci c
problem of multi-image and multi-organ problem.
5.3</p>
      <p>Complementary results on images detailed by organs
The following table 5 and graphic 4 below show the detailed scores obtained for
each type of organs. Remember that we use a speci c metric weighted by
authors and plants, and not by sub-categories, explaining why the score on images
not detailed is not the mean of the 7 scores of these sub-categories. Like during
the previous Plant Identi cation Task, the LeafScan and the Flower categories
obtained the best results, while it is not easy to rank the other organ by di
culty (maybe Fruit, Entire, Leaf, Stem, Branch). Results obtained on the Branch
category by the three last runs of IBM AU outperformed completely the other
approaches, while more shape dedicated approaches reduce the di erence with
this generic approach on LeafScan (PlantNet, Sabanki-Okan &amp; Finki).
Interestingly, the pure CNN approach in IBM AU Run 1 obtained rather good results
on Flower, the organ where there is a lot of data (as much as in the LeafScan
category in terms of number of observations), con rming the potential of the
CNN approach with more data.
6</p>
    </sec>
    <sec id="sec-6">
      <title>Conclusion</title>
      <p>
        This paper presented the overview and the results of LifeCLEF 2014 plant
identi cation testbed following the three previous campains within ImageCLEF. The
number of participants was around 10 groups showing an interest in applying
multimedia search technologies to environmental challenges. This year the
challenge climb one step by considering multiple type of view and organs of plants
while the number of species increased from 250 to 500. Results are encouraging
by scaling state-of-the-art plant recognition technologies to a real-world
application with thousands and thousands of species might still be a di cult task.
With the emergence of more and more plant identi cation apps [
        <xref ref-type="bibr" rid="ref22">22</xref>
        ] [
        <xref ref-type="bibr" rid="ref9">9</xref>
        ], [
        <xref ref-type="bibr" rid="ref1">1</xref>
        ], [
        <xref ref-type="bibr" rid="ref27">27</xref>
        ]
and the ecological urgency to build real-world and e ective identi cation tools,
we believe that the results and working notes produced during the task will be
of high interest for the computer vision and machine learning community. A
possible evolution for a new plant identi cation task in 2015 is to extend the
task to all French ora which is estimated to around 5000 species.
      </p>
    </sec>
  </body>
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