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Transcript of Modelling molecular and inorganic data ofAmanita ponderosamushrooms using artificial neural networks
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Modelling molecular and inorganic data of Amanitaponderosa mushrooms using artificial neural networks
Catia Salvador • M. Rosario Martins •
Henrique Vicente • Jose Neves • Jose M. Arteiro •
A. Teresa Caldeira
Received: 3 January 2012 / Accepted: 9 July 2012 / Published online: 24 July 2012
� Springer Science+Business Media B.V. 2012
Abstract Wild edible mushrooms Amanita ponder-
osa Malencon and Heim are very appreciated in
gastronomy, with high export potential. This species
grows in some microclimates, namely in the southwest
of the Iberian Peninsula. The results obtained demon-
strate that A. ponderosa mushrooms showed different
inorganic composition according to their habitat and
the molecular data, obtained by M13-PCR, allowed to
distinguish the mushrooms at species level and to
differentiate the A. ponderosa strains according to
their location. Taking into account, on the one hand,
that the characterisation of different strains is essential
in further commercialisation and certification process
and, on the other hand, the molecular studies are quite
time consuming and an expensive process, the devel-
opment of formal models to predict the molecular
profile based on inorganic composition comes to be
something essential. In the present work, Artificial
Neural Networks (ANNs) were used to solve this
problem. The ANN selected to predict molecular
profile based on inorganic composition has a 6-7-14
topology. A good match between the observed and
predicted values was observed. The present findings
are wide potential application and both health and
economical benefits arise from this study.
Keywords Ectomycorrhizal macrofungi �Wild
edible mushrooms � M13-PCR � Inorganic
composition � Artificial intelligence based tools
Introduction
Amanita ponderosa (Malencon and Heim 1942) are
wild edible mushroom, growing in some mediterra-
nean microclimates, in the southwest of the Iberian
Peninsula, due to its mediterranean characteristics,
namely in Alentejo (Portugal) and Andalusia (Spain),
Morocco and very rare in Italy (Moreno et al. 2008).
C. Salvador � H. Vicente � J. M. Arteiro �A. T. Caldeira (&)
Department of Chemistry and Evora Chemistry Centre,
University of Evora, Rua Romao Ramalho n859,
7000-671 Evora, Portugal
e-mail: [email protected]
C. Salvador
e-mail: [email protected]
H. Vicente
e-mail: [email protected]
J. M. Arteiro
e-mail: [email protected]
M. R. Martins
Chemistry Department and Institute of Mediterranean
Agricultural and Environmental Sciences, University
of Evora, Rua Romao Ramalho n859, 7000-671 Evora,
Portugal
e-mail: [email protected]
J. Neves
Department of Informatics, University of Minho,
Braga, Portugal
e-mail: [email protected]
123
Agroforest Syst (2013) 87:295–302
DOI 10.1007/s10457-012-9548-y
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It is characterised by a large and robust basidium,
with a cap 8–17 cm in diameter, a hemispheric
morphology when young and plane-convex in matu-
rity, and a slight depression in the centre (Fig. 1). The
hymenium is constituted of broad laminas, only
slightly serrated, free or subordinated, with few
lamellae, white but soon going ochraceous and red-
mottled. The stipe is cylindrical, partly smooth to
slightly fibrillose, from 7–13 cm long and 2–5 cm in
diameter, paler in colour than the cap or showing
pinkish-brown hues; it has an unclear annulus, broken
up by the growth of the carpophore, the remainder
like threads surrounding the stipe. The base of the
stem is constituted by a membranous volva, the same
colour as the rest of the fruiting body, able to become,
sac-like, half the height of the stipe. The flesh is firm,
very compact, white, but pinkish when in contact with
the air, with a pungent flavour and odour, like damp
earth. The spores are clumped or scattered and white
when fresh, cream when dry (Moreno-Rojas et al.
2004).
As far as we know there are few studies evaluating
the inorganic composition of A. ponderosa in Iberian
Peninsula. The nutritional values of these fungi make
them highly exportable. Mineral and organic compo-
sition of mushrooms depends on the ecosystem where
they grow. Mushrooms can accumulate high concen-
trations of some elements, namely toxic metals,
because of the symbiotic relation between these
macrofungi and some plants in its habitats (Vetter
2005; Kalac 2010). Therefore it is crucial to determi-
nate their inorganic content in further commercialisa-
tion process.
On the other hand, due to the wide diversity of
mushrooms in nature, it is essential to differentiate and
to identify the various edible species. Genetic profiles
and polymorphic sequences can constitute important
tools for a fast and effective characterisation, namely
in certification processes. In respect to A. ponderosa
mushrooms, existing studies are still incomplete and a
profound knowledge is quite required, especially with
regard to their correct identification and nutritional
value. Data mining tools were used in order to
establish a bridge of inorganic contents, molecular
fingerprints and geographical sites.
The conventional modelling tools have a great
number of drawbacks, since they do not allow the
prediction of singularities inside complex data.
In recent years, some artificial intelligence based
tools, namely Artificial Neural Networks (ANNs) and
Decision Trees (DTs) have been applied for fungal
environment systems (Caldeira et al. 2011a, b).
However, the establishment of a bridge between
inorganic contents, A. ponderosa molecular finger-
prints and geographical sites is a complex and highly
nonlinear problem for which, to our knowledge, no
methods have been reported in the literature.
Artificial Neural Networks (ANNs) are computa-
tional tools which attempt to simulate the architecture
and internal operational features of the human brain
and nervous system. Several types of neural networks
can be found in the literature. However, the multilayer
perceptron is the most common neural network type.
This type of networks are formed by three or more
layers of artificial neurons or nodes, the basic
computing units, which include an input layer, an
output layer and a number of hidden layers with a
certain number of active neurons connected by
feedforward links, to which are associated modifiable
weights. In addition, there is also a bias, which is
connected to neurons in the hidden and output layers.
The number of nodes in the input layer denotes the
number of independent variables and the number of
nodes in the output layer stands for the number of
dependent variables (Haykin 2008).
The aim of the current study was to use artificial
intelligence based tools, particularly ANNs to address
Fig. 1 Macroscopic aspects of edible Mushrooms A. ponder-osa in some maturity stages
296 Agroforest Syst (2013) 87:295–302
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this problem. ANNs can learn from examples, are fault
tolerant in the sense that they are able to handle noisy
and incomplete data, are able to deal with nonlinear
problems and, once trained, can perform prediction
and generalisation at high speed (Galushkin 2007;
Haykin 2008).
This work is a new approach for the A. ponderosa
species, since until now no study was performed
concerning both trace metals composition and molec-
ular identification.
Materials and methods
Sample collection and preservation
Fruiting bodies of the A. ponderosa mushrooms were
collected in spring, between February and April 2010,
from six different location areas, in the southwest of
the Iberian Peninsula, namely Evora, Beja, Mina de
Sao Domingos, Santo Aleixo da Restauracao and Vila
Nova de Sao Bento (Alentejo, Portugal) and from
Cabezas Rubias (Andalusia, Spain). The mushrooms
under analysis were collected in acid soils, in forests of
Quercus suber, Q. ilex ssp. ballota, Cistus ladanifer
and Cistus laurifolius of the abovementioned sites, at
the same growth stage to avoid the effect of size.
Fruiting bodies were identified by a specialist, based
on morphological features according to taxonomic
description of A. ponderosa (Malencon and Heim
1942).
Three individuals were sampled per location. The
material was weighed and placed in sterile bags for its
inorganic study and molecular characterisation. For
the microsatellite primer M13-PCR molecular study,
the A. ponderosa strains were compared with other
Basidiomycetes (Pleurotus ostreatus and Lactarius
deliciosus) and with one Ascomycete strain (Terfezia
arenaria syn. Tuber arenaria).
Inorganic characterisation
The inorganic contents (Ca, Mg, Fe, Cu, Zn, Mn, Na,
K and P), of A. ponderosa samples were analysed
according to Moreno-Rojas et al. (2004).
Data was evaluated statistically using the SPSS�
16.0 software, by descriptive parameters and by One-
way ANOVA, followed by Tukey test.
Molecular analyses
The genomic DNA extraction from the small frag-
ments of fruiting bodies was performed by the
modified microsphere method (Martins 2004). DNA
amplification was carried out with M13 primer
(50-GAGGGTGGCGGTTCT-30), as described by
Caldeira et al. (2009).
Phylogenetic tree was generated by the UPGMA
method, using the Dice coefficient of similarity.
ANNs
In this study the most common neural network type,
the multilayer perceptron, was adopted. In the training
phase, the backpropagation algorithm (Rumelhart
et al. 1986) was applied. In all experiments, the
sigmoid activation function was used:
u uj
� �¼ 1
1þ e�uj
where uj denotes the weighted sum of the j th neuron
for the input received from a former layer with n
neurons, calculated as:
uj ¼Xn
i¼1
wijxi þ biasj
where wij denotes the weight between the j th neuron
and the i th neuron in the preceding layer, xi denotes
the output of the i th neuron in the preceding layer and
biasj denotes the weight between the j th neuron and
the bias neuron in the preceding layer.
It was used the Waikato Environment for Knowl-
edge Analysis (WEKA) (Hall et al. 2009) to imple-
ment ANNs keeping the default software parameters.
The methodology adopted started with a small
network and continued by adding nodes to improve
performance i.e. in order to minimise an error metric
(Han and Kamber 2006).
To ensure statistical significance of the attained
results, 20 runs were applied in all tests. In each
simulation, the available data was randomly divided into
three mutually exclusive partitions: the training set, with
60 % of the available data, used during the modelling
phase, the test set, with 25 % of the examples, used after
training in order to evaluate the model performance, and
the validation set, with the remaining 15 % of data, to
validate the models (Souza et al. 2002).
Agroforest Syst (2013) 87:295–302 297
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Results and discussion
Mineral composition
Results of mineral content of the selected A. ponder-
osa strains are described in Table 1.
The ANOVA one-way analysis showed that min-
eral contents of A. ponderosa strains were statistically
significant (p \ 0.001) for all elements investigated.
Tukey post hoc test allows correlating the strains from
different areas and make in evidence homogeneous
groups, based on the similarity of the strains, for each
mineral content (p \ 0.001). Potassium was the
element present in higher concentration in all Amanita
strains, the Cabezas Rubias strains show the highest
value, on the other hand, Mn was the element with
lower values and Santo Aleixo da Restauracao strains
presented the lowest value. Ca contents were signif-
icantly different between A. ponderosa strains from
Santo Aleixo da Restauracao, Beja, Evora and Cabe-
zas Rubias (p \ 0.001), but do not present significant
differences for the strains collected from Mina de Sao
Domingos and Vila Nova de Sao Bento (p = 0.377).
Mg contents were significantly different for mush-
rooms collected from the different areas (p \ 0.001)
except for the strains from Evora and Vila Nova de Sao
Bento (p = 1). Zn, Cu, Fe, Mn and K levels were
significantly different for the six A. ponderosa strains
tested (p \ 0.001). Na content showed significant
differences between location areas, except for Evora
and Mina de Sao Domingos strains (p = 0.607). P
contents also showed significant differences between
location areas, except for Evora and Beja (p = 0.121).
As far as we know there are few studies evaluating
the inorganic composition of A. ponderosa in Iberian
Peninsula. A profound technical knowledge is
required for a product that is so eagerly consumed,
especially with regard to its correct identification and
nutritional value. Trace elements like Fe, Cu, Zn and
Mn play an important role in biological systems (FAO/
WHO 2002); however, they can also produce toxic
effects when the metal intake is excessively (Sesli
et al. 2008). Fe values obtained in this study were
lower than those reported in the literature (Ouzouni
et al. 2007). Cu levels were near those related for
Amanita spp. whereas lower than others edibles mush-
rooms species reported in the literature (Moreno-Rojas
et al. 2004; Sesli et al. 2008). Cu levels were near those
related for Amanita spp. whereas lower than others Ta
ble
1M
iner
alco
nte
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Ca
(mg
/Kg
)3
6.7
82
±0
.08
6a
61
.40
5±
0.1
25
b5
5.4
67
±0
.12
6c
61
.20
9±
0.1
23
b5
7.1
99
±0
.11
9d
28
8.0
19
±0
.12
0e
Mg
(mg
/Kg
)4
8.4
08
±0
.02
7a
67
.41
0±
0.0
39
b6
6.2
23
±0
.03
9c
77
.47
5±
0.0
77
d6
7.4
07
±0
.07
4b
10
3.3
97
±0
.07
5e
Zn
(mg
/Kg
)4
.69
3±
0.0
08
a8
.84
0±
0.0
11
b9
.39
5±
0.0
11
c9
.58
5±
0.0
11
d7
.10
4±
0.0
10
e1
0.7
63
±0
.01
1f
Cu
(mg
/Kg
)1
2.9
31
±0
.01
4a
17
.68
6±
0.0
20
b3
3.6
50
±0
.02
0c
35
.11
4±
0.0
20
d1
8.7
27
±0
.01
9e
11
.48
1±
0.0
19
f
Fe
(mg
/Kg
)5
.08
3±
0.0
21
a1
8.6
10
±0
.03
0b
20
.46
9±
0.0
61
c6
.49
1±
0.0
30
d2
7.6
02
±0
.05
8e
15
.79
9±
0.0
29
f
Mn
(mg
/Kg
)4
.72
7±
0.0
06
a7
.33
6±
0.0
08
b7
.57
2±
0.0
08
c1
0.9
28
±0
.00
8d
5.5
94
±0
.00
8e
6.6
21
±0
.00
8f
K(m
g/K
g)
1,8
70
.00
0±
10
.62
5a
63
8.8
67
±3
.07
1b
54
9.7
46
±3
.08
8c
3,5
35
.08
6±
18
.22
2d
3,2
72
.85
5±
17
.59
6e
5,6
87
.65
3±
29
.62
3f
Na
(mg
/Kg
)1
10
.50
0±
1.0
63
a1
50
.50
2±
1.5
36
b1
38
.98
1±
1.5
44
c1
15
.40
7±
1.5
19
a1
17
.30
7±
1.4
66
a2
16
.24
9±
1.4
81
d
P(m
g/K
g)
3.3
79
±0
.07
4a
20
.17
1±
0.1
38
b1
9.1
70
±0
.03
9c
15
.67
6±
0.1
00
d1
8.9
64
±0
.09
7c
5.9
80
±0
.04
9e
No
teA
lld
ata
are
sho
wn
asav
erag
em
edia
nv
alu
es(n
=1
8)
±S
E
Dif
fere
nt
sup
ersc
rip
tle
tter
sin
the
sam
ela
ne
ind
icat
esi
gn
ifica
nt
dif
fere
nce
sat
99
.9%
(p\
0.0
01
)le
vel
(AN
OV
A,
Tu
key
test
)
298 Agroforest Syst (2013) 87:295–302
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edibles mushrooms species reported in the literature
(Sesli et al. 2008; Moreno-Rojas et al. 2004). Present
Cu concentrations in mushrooms are not considered a
health risk (Commission 2003). Zn is an element with
biological properties that can be accumulated by
mushrooms (Mendil et al. 2004). Results showed that
Zn and Mn content were near for those related by
Moreno-Rojas et al. (2004) for A. ponderosa strains
although lower than those reported for others edible
mushrooms (Kalac and Svoboda 2000).
Molecular analyses
M13-PCR fingerprinting of different A. ponderosa
strains assayed generated different patterns with 8–20
bands, ranging from 260 to 1,490 bp. A. ponderosa
band profiles were compared with other edible mush-
rooms namely Pleurotus ostreatus and Lactarius
deliciosus and with one wild edible truffle Terfezia
arenaria. Dendrogram molecular analysis shows three
different clusters (Fig. 2). Cluster A illustrate that T.
arenaria, an ectomycorrhizal ascomycete, is the most
distant species from the remaining strains (40 % of
similarity). Cluster B was obtained for L. deliciosus
and P. ostreatus (similarity of 49 %) and cluster C
grouped all A. ponderosa strains (67 % of similarity).
This approach although producing band profiles very
similar for the A. ponderosa strains is able to detect
intraspecific variation, showing different polymor-
phisms between strains of the same species. The most
similar strains, from Evora and Santo Aleixo da
Restauracao, forming a cluster with 85 % of similar-
ity, while strains collected from Beja, Vila Nova de
Sao Bento and Cabezas Rubias give another cluster
with 80 % of similarity (Fig. 2).
Literature related a range of molecular approaches
based on RAPD analyses in order to characterise and
identify edible mushrooms (Moncalvo et al. 2000;
Firenzuoli et al. 2007), however, a lack of information
to A. ponderosa mushrooms is verified, only one study
is reported to distinguish A. curtipes and A. ponderosa
species sequencing the D1–D2 domains of the 28S
rRNA gene and ITS1-5.8S-ITS2 region (Moreno et al.
2008). Previous studies performed with seven micro-
satellite primers showed that the M13-PCR approach
is a rapid and precise method that allows differenti-
ation at the species and strain level (Caldeira et al.
2009).The M13 primer were also used to study genetic
variability in yeasts and filamentous fungi species
(Alves et al. 2007; Lopes et al. 2007). Actually, M13-
PCR technique is easy to implement, less time-
consuming than other molecular approaches with
restriction enzymes. It is highly reproducible and is
much more robust than RAPD-PCR for species
Fig. 2 Dendrogram analysis based on the M13-PCR for A.ponderosa strains and other wild edible mushrooms
Table 2 The main fields in the dataset
Mineral
composition
DNA fragments
(bp)
Location area
Ca 422.54 Evora
Mg 609.77 Beja
Zn 723.42 Mina de Sao
Domingos
Cu 786.26 Santo Aleixo da
Restauracao
Fe 856.72 Vila Nova
de Sao Bento
Mn 1,090.20 Cabezas Rubias
K 1,189.66
Na
P
Agroforest Syst (2013) 87:295–302 299
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identification by visual analysis of the amplification
patterns.
Modelling
Database
The data used in this study containing a total of 108
records with 17 fields. Table 2 shows a synopsis of the
relevant fields of the dataset. The main fields in the
dataset were the mineral composition of A. ponderosa
strains, M13-PCR band profile and the locations in
which the samples were collected. For the molecular
analysis characterisation, the indicators chosen were
the presence or the absence of the bp DNA fragments
(Table 2).
ANN model
Artificial neural networks were used to predict the
M13-PCR DNA band profile from A. ponderosa based
on inorganic composition of the mushrooms.
The ANN model obtained is showed in Fig. 3. The
architecture of the model consists in an input layer
with six nodes, a hidden layer with seven and a 14
nodes output layer.
It should be emphasised that the algorithm chooses
only six mineral composition variables (Cu, Fe, K,
Mn, Na, Zn), even though all the mineral composition
variables presented in Table 1 were available for use.
In order to evaluate the model output sensitivity to
changes in its input variables it was used the sensitiv-
ity, according to the variance (Kewley et al. 2000), to
compute the relative importance of the input variables.
The results are presented in Fig. 4 and reveal that the
most informative variable is Zn followed by Fe and
Cu. These results seem to suggest that these three
variables have direct relevance and play a significant
role in the M13-PCR DNA band profile from A.
ponderosa. Table 3 presents the coincidence matrix
for the model. The values denote the average of the 20
Fig. 3 Artificial neural networks model Fig. 4 Relative importance of input variables
300 Agroforest Syst (2013) 87:295–302
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runs. The results reveal that the model exhibits
accuracy of 100 % in predicting M13-PCR DNA
band profile from A. ponderosa for training set, test set
and validation set.
Conclusions
M13-PCR allows to distinguish the molecular profiles
from A. ponderosa strains collected from different
location areas and the inorganic analyses showed that
mineral composition of mushrooms depends on the
ecosystem where they grow. The results show that it was
possible to correlate the molecular and inorganic data.
It would be interesting to study, in parallel, the
concentration of minerals in soils from the different
locations in order to distinguish substrate effects from
inter-individual or inter-strain differences.
The present findings are wide potential application
and both health and economical benefits arise from
this study.
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Table 3 The coincidence matrix for ANN model
Training set Test set Validation
A P A P A P
1,190 bp DNA fragment
A 30 0 16 0 8 0
P 0 34 0 12 0 8
1,090 bp DNA fragment
A 53 0 24 0 13 0
P 0 11 0 4 0 3
857 bp DNA fragment
A 21 0 11 0 4 0
P 0 43 0 17 0 12
786 bp DNA fragment
A 53 0 24 0 13 0
P 0 11 0 4 0 3
723 bp DNA fragment
A 53 0 24 0 13 0
P 0 11 0 4 0 3
610 bp DNA fragment
A 21 0 11 0 4 0
P 0 43 0 17 0 12
423 bp DNA fragment
A 41 0 20 0 11 0
P 0 23 0 8 0 5
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