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International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017
http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878
www.ijeab.com Page | 1557
Comparison between Manual and Automatic
Identification of Diatoms of Merja Fouarate
(Morocco)
Nouzha Chahboune, Mohamed Mehdi, Allal Douira
Université Ibn Tofail, Faculté des Sciences, Laboratoire de Botanique, Biotechnologie et de Protection des Plantes, B.P. 133,
Kenitra, Marocco
Abstract— The objective of this work is to compare the
results of the classical identification of diatoms by optical
microscope to the automatic identification of the diatoms.
For the first method, we determined the diatoms using an
optical microscope and the identification keys.
Concerning the second method, we relied on the processing
and analysis of the images to automatically recognize a
diatom. Our aim is to compare the results of the manual
identification of diatoms with the results of the automatic
identification of the same sample. The purpose of this
comparison is to verify whether the automaticanalysis can
give acceptable results in order to replace the manual
determination. We used the Image j software for the
development of our program and based on the notion of
points of interest and the freeman code.
The results of the determination of the diatoms by optical
microscope which lasted more than one month did not
exceed 92% (for 104 species of diatoms 96 species were
identified), whereasthe automatic identificationrequires
only a few seconds, with much better results (97%).
Keywords— Diatoms, current, identification by
microscope, automatic identification, digital image
processing, Fouarate, Kenitra, Morocco.
I. INTRODUCTION
Rich in thousands of species (Mollo and Noury, 2013),
diatoms are diversified into several groups, genera and
species, and have been the subject of extensive discussions
and divergent opinions concerning the taxonomy and
nomenclature (Tolomio, 2011). This diversification presents
morphological variations making the identification of
diatoms by optical microscope tedious (J. Prigiel and Coste,
1993; Chahboune et al., 2015; Siddour et al., 2007;
Manoylov. 2014) and heavy for the uninitiated. Automatic
image recognition provides a valuable help both for the
identification of diatoms (Chahboune et al., 2015), and
especially as a teaching tool to help in identification for new
diatomists.
Our study aimed to use two identification methods of the
diatoms of the Merja Fouarat, one is the classical method
which is based on the identification key using the optical
microscope, the other is the automatic method which relies
on image analysis and interpretation techniques. The
comparison of the two methods allowed us to define to what
extent the automatic identification method can meet the
challenges encountered in order to identify the diatoms
precisely and in a very short time.
II. MATERIALS AND METHODS
1- Characteristics of the study sites
Located on the plateau of Mamora, between the pli-
quaternary clay plain of the Rharb and the granitic,
paleozoic , western schisto-sandstone Meseta, the Merja
Fouarat is the site of a water table located in the sand and
limestone sand of the Plio-Villafranchien (Combe, 1975),
with Mediterranean climate and pronounced oceanic
influence (sub-humid low temperature, temperate in
winter).
The MerjaFouarat is fed by:
- The inflows of Oued Fouarat representing the first
important valley of the Mamora plateau (Thauvin, 1966)
with a source located at Ras-El-Aîn, about 10 km south of
the Merja;
- Abundant and close rainfalls lead to the exfiltration of
natural water from the groundwater (Nassali et al., 2002),
accompanied by short duration floods;
- Wastewater from peripheral neighborhoods.
International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017
http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878
www.ijeab.com Page | 1558
Fig.1: Location of study sites
Caption: S1: Reference station: (Oued Fouarat)
S2, S3, S4 and S5: Stations along the Merja
Fouarat
2- Sampling
At the five stations, three diatom sampling campaigns were
performed. The diatoms were removed by scratching
natural substrates using a nylon bristle brush. The samples
thus obtained were immediately fixed in formalin (10%).
After a few days of decantation, the diatoms were treated
with nitric acid on a hot-plate then mounted with naphrax
between the blade and the lamella.
3- Identification of diatoms
The identification of diatoms by optical microscope was
carried out with the help of the work of Germain, 1981;
Krammer and Langbertalot, 1986, 1988, 1991a and b). The
optical microscopic counts of at least 450 frustules were
performed on permanent preparations. The numbers of each
taxon were transformed into relative abundance
(Chahboune et al., 2011). The automatic identification
consisted of a classification from the same sample. This
identification relied on the software Image j (Chahboune et
al., 2015), a digital image processing application developed
at the National Institute of Health (Wayne, 1997).
III. RESULTS AND DISCUSSION
The identification of the diatoms by microscope required an
enormous effort both in terms of learning, which lasted five
months in order to acquire the skills of a diatomist, and in
terms of the determination of the diatoms which lasted
longer than a month with a result approaching 92%, for 96
diatom species out of 104. 8 species (Navicula sp 1,
Navicula sp2, Navicula sp3, Nitzschia sp1, Nitzschia sp2,
Gomphonema sp1, Gomphonema sp2, Surerella) were
difficult to classify. Indeed, the particularities of some
potentially more complex species are difficult to solve
(Tolomio, 2011; Ector and DašaHlúbiková, 2010; Lavoie,
2008; Coste and Ector, 2000).
The automatic identification in turn required a pre-
processing phase of the images and the results were around
97%. The automatic classification work confirms our
approach:
 ADIAC teams have achieved good classification
rates above 96% on a much larger sample, even
surpassing the results of human experts. (Jalba et
al., 2004).
 The work of (Siddour et al., 2007) which
consisted in characterizing the contour of the
diatoms according to a vector of the Fourier
descriptors from a database of diatom images,
obtained a good classification rate of 97%. As for
(Claudon, 2007), he presented a classification
method based also on the windowed Fourier
transform, but taking into account the internal
structures and the ornamentations of the diatoms.
His analysis on a reference sample was
approaching 100%.
Therefore, we find that the automatic classification is
effective. However, the automatic recognition of diatoms is
a long term project because its success requires that the
image database be continuously supplied. Clearly, the
system we have developed can only identify the diatoms
listed. If a diatom does not exist in the database, it will not
be recognized. Further work should help fuel the image
database.
IV. CONCLUSION
We can infer that automation has a double contribution: it
allows a rapid identification with great success results, and
especially allows the novice to avoid a tedious learning.
REFERENCES
[1] Chahboune N., Mehdi M. & Douira A., 2015.
Identification automatique des diatomées de la Merja
Fouarate : Une alternative à la détermination et à la
classification manuelle. Journal of Applied
Biosciences, 93:8675–8687.
International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017
http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878
www.ijeab.com Page | 1559
[2] Chahboune N., Mehdi M. & Douira A., 2011.
Détérioration des écosystèmes aquatiques dans la
région du gharb (Maroc) : Analyse diatomique
.Science lib Éditions Mersenne: volume 3, N ° 110808
ISSN 2111-4706.
[3] Claudon N. 2007. Automatic classification of
diatomies: an approach to the patterns of internal
structures. Mémoire présenté à l'université du Québec
à Trois-Rivières.Université du Québec
[4] Combe M., 1975: Le bassin Rharb-Maamora.
Ressources en eau de la plaine du Rharb et bassins du
Maroc atlantique. Notes et Mémoires du Service
Géologique, Maroc, N° 231.
[5] Coste M. and Ector L., 2000. Diatomées invasives
exotiques ou rares en France: Principales Observations
effectuées au cours des dernières décennies.
Systematics and Geography of Plants, 70(2), 373-400.
[6] Germain H., 1981. Flore des diatomées,
Diatomophycées. Paris, Boubée, 444p.
[7] Jalba Andrei C., Michael H.F. Wilkinson & Jos
B.T.M. Roerdink, 2004. Automatic Segmentation of
Diatom Images for classification. Microscopy
Research and Technique, 65:72– 85
[8] Krammer K. & Langebertalot H., 1986.
Bacillariophyceae. Tome 1: Naviculaceae. Semper
Bonis Artibus, 876p.
[9] Krammer K & Langebertalot H., 1988.
Bacillariophyceae, Tome 2: Bacillariaceae,
Epithemiaceae et Surirellaceae. Semper Bonis Artibus,
596p.
[10]Krammer K & Langebertalot H., 1991a.
Bacillariophyceae. Tome 3: Centrales,Fragilariaceae,
Eunotiaceae. Semper Bonis Artibus, 576p.
[11]Krammer K. & Langebertalot H., 1991b.
Bacillariophyceae. Tome 4: Achnanthaceae. Semper
BonisArtibus, 437p.
[12]Krammer K. & Langebertalot H., 2000.
Bacillariophyceae. Tome 5: Englishand French
translation of the Keys. Semper Bonis Artibus, 311p.
[13]Lavoie I., 2008. Guide des diatomées des rivières de
l’est de Canada. Presse de l’université de Québec,
2ème trimestre, 450 p.
[14]Ector Luc & Dasa Hlubicova, 2010 : Atlas des
diatomées des Alpes-Maritimes et de la Région
Provence-Alpes-Côte d’Azur. Conseil Général des
Alpes-Maritimes, Direction de l’Écologie et du
Développement Durable Sous-Direction Ingénierie
Environnementale et Expertise Service Eaux et Milieu
marin, 393 p.
[15]Manndg Vanormelingen P., 2013.An Inordinate
Fondness,The Number, Distributions, and Origins of
Diatom Species. Journal of Eukaryotic Microbiology,
60: 414-420.
[16]Manoylov K.M., 2014: Taxonomic identification of
algae (morphological and molecular): species
concepts, methodologies, and their implications for
ecological bioassessment. Journal of Phycology, 50:
409-424.
[17]Prygiel J. & Coste M., 2000.Guide méthodologique
pour la mise en œuvre de l’Indice Biologique
Diatomées NF T 90-354, Agences de l’Eau-Cemagref.
[18]Siddour A., Nouboud F., Mammass D., Chalifour
A., Campeau S., 2007. Classification of diatoms by
contour Fourier descriptors. Numéro 4 / Issue 4.
Spécial MCSEAI 2006 > Recherche de formes et
vision / Pattern Recognition and Vision
http://www.revue-eti.net/document.php?id=1374.
[19]Tolomio C., 2011 : Inventaire préliminaire du
phytoplancton de la Corse en saison estivale (Baie de
Calvi et Golfe de Porto Vecchio). Marinelife, revue.fr,
17 : 25- 38.

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Comparison between Manual and Automatic Identification of Diatoms of Merja Fouarate (Morocco)

  • 1. International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017 http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878 www.ijeab.com Page | 1557 Comparison between Manual and Automatic Identification of Diatoms of Merja Fouarate (Morocco) Nouzha Chahboune, Mohamed Mehdi, Allal Douira Université Ibn Tofail, Faculté des Sciences, Laboratoire de Botanique, Biotechnologie et de Protection des Plantes, B.P. 133, Kenitra, Marocco Abstract— The objective of this work is to compare the results of the classical identification of diatoms by optical microscope to the automatic identification of the diatoms. For the first method, we determined the diatoms using an optical microscope and the identification keys. Concerning the second method, we relied on the processing and analysis of the images to automatically recognize a diatom. Our aim is to compare the results of the manual identification of diatoms with the results of the automatic identification of the same sample. The purpose of this comparison is to verify whether the automaticanalysis can give acceptable results in order to replace the manual determination. We used the Image j software for the development of our program and based on the notion of points of interest and the freeman code. The results of the determination of the diatoms by optical microscope which lasted more than one month did not exceed 92% (for 104 species of diatoms 96 species were identified), whereasthe automatic identificationrequires only a few seconds, with much better results (97%). Keywords— Diatoms, current, identification by microscope, automatic identification, digital image processing, Fouarate, Kenitra, Morocco. I. INTRODUCTION Rich in thousands of species (Mollo and Noury, 2013), diatoms are diversified into several groups, genera and species, and have been the subject of extensive discussions and divergent opinions concerning the taxonomy and nomenclature (Tolomio, 2011). This diversification presents morphological variations making the identification of diatoms by optical microscope tedious (J. Prigiel and Coste, 1993; Chahboune et al., 2015; Siddour et al., 2007; Manoylov. 2014) and heavy for the uninitiated. Automatic image recognition provides a valuable help both for the identification of diatoms (Chahboune et al., 2015), and especially as a teaching tool to help in identification for new diatomists. Our study aimed to use two identification methods of the diatoms of the Merja Fouarat, one is the classical method which is based on the identification key using the optical microscope, the other is the automatic method which relies on image analysis and interpretation techniques. The comparison of the two methods allowed us to define to what extent the automatic identification method can meet the challenges encountered in order to identify the diatoms precisely and in a very short time. II. MATERIALS AND METHODS 1- Characteristics of the study sites Located on the plateau of Mamora, between the pli- quaternary clay plain of the Rharb and the granitic, paleozoic , western schisto-sandstone Meseta, the Merja Fouarat is the site of a water table located in the sand and limestone sand of the Plio-Villafranchien (Combe, 1975), with Mediterranean climate and pronounced oceanic influence (sub-humid low temperature, temperate in winter). The MerjaFouarat is fed by: - The inflows of Oued Fouarat representing the first important valley of the Mamora plateau (Thauvin, 1966) with a source located at Ras-El-Aîn, about 10 km south of the Merja; - Abundant and close rainfalls lead to the exfiltration of natural water from the groundwater (Nassali et al., 2002), accompanied by short duration floods; - Wastewater from peripheral neighborhoods.
  • 2. International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017 http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878 www.ijeab.com Page | 1558 Fig.1: Location of study sites Caption: S1: Reference station: (Oued Fouarat) S2, S3, S4 and S5: Stations along the Merja Fouarat 2- Sampling At the five stations, three diatom sampling campaigns were performed. The diatoms were removed by scratching natural substrates using a nylon bristle brush. The samples thus obtained were immediately fixed in formalin (10%). After a few days of decantation, the diatoms were treated with nitric acid on a hot-plate then mounted with naphrax between the blade and the lamella. 3- Identification of diatoms The identification of diatoms by optical microscope was carried out with the help of the work of Germain, 1981; Krammer and Langbertalot, 1986, 1988, 1991a and b). The optical microscopic counts of at least 450 frustules were performed on permanent preparations. The numbers of each taxon were transformed into relative abundance (Chahboune et al., 2011). The automatic identification consisted of a classification from the same sample. This identification relied on the software Image j (Chahboune et al., 2015), a digital image processing application developed at the National Institute of Health (Wayne, 1997). III. RESULTS AND DISCUSSION The identification of the diatoms by microscope required an enormous effort both in terms of learning, which lasted five months in order to acquire the skills of a diatomist, and in terms of the determination of the diatoms which lasted longer than a month with a result approaching 92%, for 96 diatom species out of 104. 8 species (Navicula sp 1, Navicula sp2, Navicula sp3, Nitzschia sp1, Nitzschia sp2, Gomphonema sp1, Gomphonema sp2, Surerella) were difficult to classify. Indeed, the particularities of some potentially more complex species are difficult to solve (Tolomio, 2011; Ector and DašaHlúbiková, 2010; Lavoie, 2008; Coste and Ector, 2000). The automatic identification in turn required a pre- processing phase of the images and the results were around 97%. The automatic classification work confirms our approach:  ADIAC teams have achieved good classification rates above 96% on a much larger sample, even surpassing the results of human experts. (Jalba et al., 2004).  The work of (Siddour et al., 2007) which consisted in characterizing the contour of the diatoms according to a vector of the Fourier descriptors from a database of diatom images, obtained a good classification rate of 97%. As for (Claudon, 2007), he presented a classification method based also on the windowed Fourier transform, but taking into account the internal structures and the ornamentations of the diatoms. His analysis on a reference sample was approaching 100%. Therefore, we find that the automatic classification is effective. However, the automatic recognition of diatoms is a long term project because its success requires that the image database be continuously supplied. Clearly, the system we have developed can only identify the diatoms listed. If a diatom does not exist in the database, it will not be recognized. Further work should help fuel the image database. IV. CONCLUSION We can infer that automation has a double contribution: it allows a rapid identification with great success results, and especially allows the novice to avoid a tedious learning. REFERENCES [1] Chahboune N., Mehdi M. & Douira A., 2015. Identification automatique des diatomées de la Merja Fouarate : Une alternative à la détermination et à la classification manuelle. Journal of Applied Biosciences, 93:8675–8687.
  • 3. International Journal of Environment, Agriculture and Biotechnology (IJEAB) Vol-2, Issue-4, July-Aug- 2017 http://dx.doi.org/10.22161/ijeab/2.4.14 ISSN: 2456-1878 www.ijeab.com Page | 1559 [2] Chahboune N., Mehdi M. & Douira A., 2011. Détérioration des écosystèmes aquatiques dans la région du gharb (Maroc) : Analyse diatomique .Science lib Éditions Mersenne: volume 3, N ° 110808 ISSN 2111-4706. [3] Claudon N. 2007. Automatic classification of diatomies: an approach to the patterns of internal structures. Mémoire présenté à l'université du Québec à Trois-Rivières.Université du Québec [4] Combe M., 1975: Le bassin Rharb-Maamora. Ressources en eau de la plaine du Rharb et bassins du Maroc atlantique. Notes et Mémoires du Service Géologique, Maroc, N° 231. [5] Coste M. and Ector L., 2000. Diatomées invasives exotiques ou rares en France: Principales Observations effectuées au cours des dernières décennies. Systematics and Geography of Plants, 70(2), 373-400. [6] Germain H., 1981. Flore des diatomées, Diatomophycées. Paris, Boubée, 444p. [7] Jalba Andrei C., Michael H.F. Wilkinson & Jos B.T.M. Roerdink, 2004. Automatic Segmentation of Diatom Images for classification. Microscopy Research and Technique, 65:72– 85 [8] Krammer K. & Langebertalot H., 1986. Bacillariophyceae. Tome 1: Naviculaceae. Semper Bonis Artibus, 876p. [9] Krammer K & Langebertalot H., 1988. Bacillariophyceae, Tome 2: Bacillariaceae, Epithemiaceae et Surirellaceae. Semper Bonis Artibus, 596p. [10]Krammer K & Langebertalot H., 1991a. Bacillariophyceae. Tome 3: Centrales,Fragilariaceae, Eunotiaceae. Semper Bonis Artibus, 576p. [11]Krammer K. & Langebertalot H., 1991b. Bacillariophyceae. Tome 4: Achnanthaceae. Semper BonisArtibus, 437p. [12]Krammer K. & Langebertalot H., 2000. Bacillariophyceae. Tome 5: Englishand French translation of the Keys. Semper Bonis Artibus, 311p. [13]Lavoie I., 2008. Guide des diatomées des rivières de l’est de Canada. Presse de l’université de Québec, 2ème trimestre, 450 p. [14]Ector Luc & Dasa Hlubicova, 2010 : Atlas des diatomées des Alpes-Maritimes et de la Région Provence-Alpes-Côte d’Azur. Conseil Général des Alpes-Maritimes, Direction de l’Écologie et du Développement Durable Sous-Direction Ingénierie Environnementale et Expertise Service Eaux et Milieu marin, 393 p. [15]Manndg Vanormelingen P., 2013.An Inordinate Fondness,The Number, Distributions, and Origins of Diatom Species. Journal of Eukaryotic Microbiology, 60: 414-420. [16]Manoylov K.M., 2014: Taxonomic identification of algae (morphological and molecular): species concepts, methodologies, and their implications for ecological bioassessment. Journal of Phycology, 50: 409-424. [17]Prygiel J. & Coste M., 2000.Guide méthodologique pour la mise en œuvre de l’Indice Biologique Diatomées NF T 90-354, Agences de l’Eau-Cemagref. [18]Siddour A., Nouboud F., Mammass D., Chalifour A., Campeau S., 2007. Classification of diatoms by contour Fourier descriptors. Numéro 4 / Issue 4. Spécial MCSEAI 2006 > Recherche de formes et vision / Pattern Recognition and Vision http://www.revue-eti.net/document.php?id=1374. [19]Tolomio C., 2011 : Inventaire préliminaire du phytoplancton de la Corse en saison estivale (Baie de Calvi et Golfe de Porto Vecchio). Marinelife, revue.fr, 17 : 25- 38.