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Contents lists available at ScienceDirect
Chemie der Erde
journal homepage: www.elsevier.de/chemer
Relationship among geochemical elements in soil and grapes as
terroir fingerprintings in Vitis vinifera L. cv. “Glera”
Salvatore Pepi a,∗ , Luigi Sansone b , Milvia Chicca c , Carmela Vaccaro a
a
Department of Physics and Earth Sciences, University of Ferrara, Via Saragat 1, 44121 Ferrara, Italy
CREA, Consiglio per la ricerca in agricoltura e l’analisi dell’economia agraria, Centro di ricerca per la viticoltura, Via XXVIII Aprile 26, 31015 Conegliano,
Italy
c
Department of Life Science and Biotechnologies, University of Ferrara, Via L. Borsari 46, 44121 Ferrara, Italy
b
a r t i c l e
i n f o
Article history:
Received 9 March 2016
Received in revised form
19 September 2016
Accepted 8 January 2017
Keywords:
LDA
Grape
Fingerprints
Prosecco
XRF
ICP-MS
Trace elements
Veneto
Geo-lithology
a b s t r a c t
Prosecco, one of the most popular sparkling wines in the world, is produced in Italy. For this reason, it is
important to develop a scientific method for determining geographic origin in order to prevent fraudulent
labelling. To establish the relationship between geochemistry of vineyard soil and chemical composition
of grape, a geochemical characterization of “Glera”, a Vitis vinifera cultivar from Italian Region, Veneto
was undertaken. We evaluated the relationship between major and trace elements in soil and their
concentrations in “Glera” grape berries in vineyards belonging to five localities in the Veneto alluvial
plain, all included in the Controlled Designation of Origin (DOC) area of Prosecco. A statistically significant
correspondence between the soil and grape was observed for Sr. Multivariate analysis (LDA) allowed
discrimination of samples of soil and grape berries from each single winery according to the geographic
origin. The elements that could establish a reliable correspondence between the geolithological features
of the vineyard soil and the chemical composition of grape berries are: Sr, Ba, Ca, Mg, Al, K, Zn, B, Ni, Co.
© 2017 Elsevier GmbH. All rights reserved.
1. Introduction
The increasing international demand for sparkling wine has
recently required more intense controls to avoid falsification and
fraudulent use of denomination labels (Lenglet, 2014). The European label “Protected Designation of Origin” (PDO) identifies a
product strictly associated to a region or location whose characteristics are bound to a specific geographical environment (Cadot
et al., 2012) within the established concept of “terroir”. The International Organization of Vine and Wine (OIV) defined the “terroir”
as “a concept which refers to an area in which collective knowledge
of the interactions between the identifiable physical and biological
environment and applied vitivinicultural practices develops, providing distinctive characteristics for the products originating from
this area” (Tomasi et al., 2010). The term describes a particular vine
linked to a wine region characterized by a specific climate area, a
geological setting, a specific wine district and typical organolep-
∗ Corresponding author at: Department of Physics and Earth Sciences, University
of Ferrara, via Saragat 1, 44121, Ferrara, Italy.
E-mail address: ppesvt@unife.it (S. Pepi).
tic characteristics of the wine. From a geological point of view, the
terroir has been defined as the geochemistry of soil, surface and
ground water, or as the characteristics of agricultural food products (quality, brand, taste) which interact with climate, soil, vine
variety and geology (Wilson, 1998; Haynes, 1999; Van Leeuwen
and Seguin, 2006; Costantini and Bucelli, 2008).
It is know that the Pinot noir, Chardonnay, and Pinot Meunier
grapes employed in the production of renowned wines as “Grand
Cru” champagne, “Premier Cru” red, and “Commune” belong to
specific geological conditions, respectively the formations “Pernand marl” (a ferruginous oolite layer of Middle-Upper Jurassic),
“Dalle nacrèe” (pearly flagstone, Middle Jurassic) and “Digonella”
(marly limestone, Middle Jurassic) (Wilson, 1998). The best white
wine of the Chablis region, France, is obtained by Chardonnay vineyards planted on Kimmeridgian limestone (Malm-Upper Jurassic)
(Huggett, 2006).
The studies on terroir are based on the concept that the chemical
elements of the soil may be transferred to the plant and afterwards
to the finished product (Greenough et al., 2005; Petrini et al., 2014;
Protano and Rossi, 2014). Previous research showed that the distribution of rare earth elements (REE) in rocks was maintained in
vineyard soil and in vine tissues (Censi et al., 2014; Pepi et al., 2016a)
http://dx.doi.org/10.1016/j.chemer.2017.01.003
0009-2819/© 2017 Elsevier GmbH. All rights reserved.
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
in Vitis vinifera L. cv. “Glera”. Chemie Erde - Geochemistry (2017), http://dx.doi.org/10.1016/j.chemer.2017.01.003
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Fig. 1. Geological map of the Veneto Region (Italy) showing the location of the five “Glera” wineries studied: “Pattarello” (1), “Bottazzo” (2), “Gaiarine” (3), “Aleandri” (4),
“Nardin” (5).
Table 1
Median concentrations of major (%) and trace elements (ppm) in soil samples of the five “Glera” vineyards, analyzed by XRF. A non-parametric multiple test (Test di KruskalWallis) was applied. n = number of samples; P-values: ns = not significant; * < 0.05; ** < 0.01; *** < 0.001. Experimental values correspond to the median ± standard deviation
(SD).
wt%
Aleandri
n=6
Bottazzo
n=6
Gaiarine
n=6
Nardin
n=6
Pattarello
n=6
p-value
SiO2
TiO2
Al2 O3
Fe2 O3
MnO
MgO
CaO
Na2 O
K2 O
P2 O5
46.2 ± 1.3
0.58 ± 0.02
11.3 ± 0.6
4.12 ± 0.21
0.08 ± 0.01
8.81 ± 0.36
25.6 ± 2.1
0.33 ± 0.05
2.53 ± 0.07
0.08 ± 0.01
47.1 ± 2.8
0.61 ± 0.1
12.5 ± 1.0
4.44 ± 0.5
0.11 ± 0.01
8.69 ± 0.7
23.4 ± 3.8
0.68 ± 0.03
2.28 ± 0.2
0.12 ± 0.02
65.0 ± 0.7
0.90 ± 0.01
16.3 ± 0.5
8.14 ± 0.7
0.11 ± 0.01
2.32 ± 0.12
4.26 ± 1.7
0.56 ± 0.01
2.29 ± 0.16
0.20 ± 0.05
60.9 ± 0.3
0.84 ± 0.01
15.0 ± 0.2
7.06 ± 0.1
0.14 ± 0.01
3.94 ± 0.1
8.82 ± 0.3
0.50 ± 0.01
2.45 ± 0.05
0.12 ± 0.03
59.9 ± 0.5
0.77 ± 0.01
19.5 ± 0.7
7.04 ± 0.4
0.12 ± 0.01
3.09 ± 0.2
4.14 ± 0.4
0.98 ± 0.02
4.16 ± 0.1
0.25 ± 0.05
***
***
***
***
***
***
***
***
***
***
ppm
Ba
Co
Cr
Ga
La
Nb
Nd
Ni
Pb
Rb
Sc
Sr
V
Y
Zr
Cu
Th
Zn
179 ± 10
16.3 ± 1.0
61.1 ± 6.1
11.6 ± 1.3
58.4 ± 1.3
8.35 ± 0.9
12.8 ± 3.4
43.8 ± 3.0
21.2 ± 8.6
54.6 ± 4.9
15.7 ± 2.2
166 ± 11
87.6 ± 5.1
10.9 ± 2.0
85.8 ± 12
37.7 ± 15
2.50 ± 1.3
43.2 ± 4.3
199 ± 22
15.8 ± 0.6
47.2 ± 7.9
12.0 ± 2.5
56.3 ± 5.8
8.80 ± 1.3
12.5 ± 2.5
26.2 ± 4.1
23.8 ± 13
46.5 ± 11
16.9 ± 2.8
160 ± 23
82.2 ± 7.9
14.2 ± 2.8
98.2 ± 11
46.2 ± 19
4.55 ± 1.6
42.8 ± 6.8
354 ± 9.1
21.7 ± 1.9
132 ± 5.9
15.5 ± 0.5
79.5 ± 2.3
16.6 ± 1.6
34.3 ± 5.4
63.9 ± 2.8
33.8 ± 6.2
108 ± 9.5
17.5 ± 2.0
100 ± 4.9
108 ± 1.4
26.9 ± 2.1
252 ± 21
142 ± 26
7.70 ± 4.3
108 ± 11.7
311 ± 8.7
24.5 ± 1.3
113 ± 3.5
15.7 ± 1.3
78.1 ± 2.7
11.6 ± 4.0
24.1 ± 5.8
60.5 ± 1.1
28.7 ± 4.3
101 ± 12
17.5 ± 2.3
106 ± 16
110 ± 2.5
17.8 ± 4.67
134 ± 33.8
49.7 ± 20.3
7.25 ± 4.4
77.7 ± 2.7
609 ± 24.3
18.2 ± 1.3
81.7 ± 6.0
21.3 ± 0.5
74.3 ± 5.1
17.1 ± 1.0
38.3 ± 3.4
33.4 ± 9.7
48.3 ± 5.9
165 ± 9.2
15.3 ± 0.9
101 ± 7.9
92.8 ± 4.4
26.9 ± 3.0
217 ± 7.4
91.2 ± 8.3
12.1 ± 5.3
112 ± 7.2
***
***
***
***
***
***
***
***
***
***
n.s
***
***
***
***
***
**
***
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
in Vitis vinifera L. cv. “Glera”. Chemie Erde - Geochemistry (2017), http://dx.doi.org/10.1016/j.chemer.2017.01.003
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3
and that the concentrations of REE changed according to species
and soil type (Wyttenbach et al., 1998; Oddone et al., 2009). Major
and trace element distribution in grape berry samples of cultivars
Moscato d’Asti and Sauvignon Blanc (Aceto et al., 2013; Censi et al.,
2014), and Lambrusco (Durante et al., 2016) has been shown to be
related to geographic origin.
Studies aimed to trace the soil-plant links through the concentration of trace elements have been focused on grapes (Angelova
et al., 1999; Jakubowski et al., 1999; Protano and Rossi, 2014; Pepi
et al., 2016b) and on wine (Almeida and Vasconcelos, 2003; Jos et al.,
2004; Coetzee et al., 2005; Martin et al., 2012). Other studies concerned the distribution of trace and ultra-trace elements in grape
skin, seeds and flesh (Cabanne and Donèche, 2003; Rogiers et al.,
2006; Bertoldi et al., 2009, 2011; Young et al., 2010; Amorós et al.,
2013; Pepi et al., 2016a).
The use of isotope ratios has also been applied alone or in association with trace element concentrations as geochemical marker
of grapes and wines from Spanish and Italian regions (Gonzaı́lvez
et al., 2011; Marengo and Aceto, 2003; Aceto et al., 2013; Petrini
et al., 2014; Baffi and Trincherini, 2016; Durante et al., 2016; Pepi
et al., 2016b). The analyses of mineral profiles in grapes are usually
conducted by atomic absorption spectroscopy (AAS), inductively
coupled plasma atomic emission spectrometry (ICP-AES) or ICPmass spectrometry (ICP-MS) (González and Pena-Méndez, 2000;
De La Guardia and Gonzalvez, 2013). A recent review emphasized
that the combination of instrumental analyses with multivariate
statistics may successfully classify grapes and wines according
to geographical origin and winemaking processes (Versari et al.,
2014).
The aim of this investigation is to establish the territorial fingerprintings of “Glera”, a Vitis vinifera cultivar from Italian Region,
Veneto, through the relationships among local geo-lithological features, geochemistry of vineyard soils and chemical composition of
grapes within the Region Veneto. This cultivar is the major one
employed in the production of the renowned Controlled Designation of Origin (DOC) wine “Prosecco”: a detailed geochemical
characterization of Glera berries could be relevant not only for territorial identification but also for prevention of fraudulent labelling.
2. Materials and methods
Sampling areas
The studied vineyards belonged to five distinct wineries located
in the Region Veneto, within the Veneto-Friuli alluvial plain (Fig. 1).
From a geological point of view, the substrate is characterized
by recent fine sediments, aged from Pleistocene to Holocene. The
sampling areas belonged to the basins of rivers Brenta (winery
Pattarello), Livenza-Tagliamento (wineries Aleandri and Nardin),
Piave (wineries Bottazzo and Gaiarine). The first three wineries
were located on clay-loam alluvial sediments, while the other two
on sandy alluvial sediments. The sampling areas are characterized
by a continental climate with annual temperature range between
11.5 ◦ C and 13.5 ◦ C and temperature average slightly above 20 ◦ C.
The rainfalls are more or less equally distributed along the year,
with averages about 800 mm/y and 1100 mm/y respectively in the
low and high alluvial plain, and about 2000 mm/y on Prealps (Barbi
et al., 2012).
Grapevines of Vitis vinifera L., cultivar “Glera”, used for the Controlled Designation of Origin (DOC) wine “Prosecco”, were grafted
on three rootstocks, 420A and Kober 5bb (Vitis berlandieri & Vitis
riparia), and Richter 110 (Vitis berlandieri & Vitis rupestris). The
vines were trained with vertically oriented canopies, according to
“Sylvoz” and “Double Guyot” pruning methods. Rows were oriented
N-S and vine spacing was 2.3 m × 1.1 m in each study site.
Fig. 2. Bivariate plots of abundances of SiO2 vs Al2 O3 (a) and CaO (b), and of Fe2 O3
vs Al2 O3 (c) in soil samples from the five “Glera” vineyards indicated in Fig. 1. Values
of oxides are expressed in %.
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
in Vitis vinifera L. cv. “Glera”. Chemie Erde - Geochemistry (2017), http://dx.doi.org/10.1016/j.chemer.2017.01.003
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Fig. 3. Bivariate plots of abundances of Rb vs Al2 O3 (a), Zr vs Al2 O3 (b), Zr vs TiO2 (c) and Cr vs Al2 O3 in soil samples from the five “Glera” vineyards indicated in Fig. 1. Values
of trace elements are expressed in ppm and values of oxides in %.
Soil sampling was carried out in the five experimental fields by
means of an Edelman auger (Eijkelkamp Soil & Water, Giesbeek,
The Netherlands). For each of the five sampling areas, six soil samples were collected at regular intervals at the depth of 60 cm and
at 50 cm of distance from the vine: each sample was collected in
triplicate. At harvest time, for each of the five sampling sites nine
vineyard samples, each containing 10 grape clusters, were freshly
picked and put in polyethylene bags at 4 ◦ C. All clusters were completely destemmed in laboratory and about 300 berries for each
sampling site for each area were immediately frozen at −20 ◦ C for
analysis.
2.2. Sample treatments
2.2.1. Soil
The soil samples were dried at 105 ◦ C for 24 h to eliminate the
hygroscopic water and then ground in an agate mortar. Afterwards,
about 4 g of grounded soil were layered in a cylinder and covered
by 15 g of powdered boric acid: the layers were then pressed by an
hydraulic press to obtain the pellets suitable for X-Ray fluorescence
(XRF). The pellets were analysed by XRF in a wavelength dispersive
spectrometer ARL ADVANT’XP (Thermo Fisher Scientific, Waltham,
Massachusetts). Simultaneously, about 0.6 g of powder from each
sample was heated for about 12 h at 1000 ◦ C, cooled and weighed
again to determine the weight loss on ignition (LOI).
2.2.2. Grape berries
®
The samples (about 300 berries each) were washed with milliQ
water (resistivity 18.2 M cm−1 ), paying attention not to damage
them in order to avoid juice loss. The samples were centrifuged at
12,600 rpm in a Centrika Metal centrifuge (Ariete, Florence, Italy)
separating the juice residue (JR) from solid residue (SR), according
to a previously established protocol (Pepi et al., 2016a,b).
A quantity of 4 g of JR was accurately weighed in a Teflon digestion vessel, capacity, 43 × 60 mm size (VWR International, Milan,
®
Italy), adding 3 mL of HNO3 (65% in distilled water, Suprapur ,
Merck KGaA, Darmstadt, Germany) and 3 mL of H2 O2 (37% in
®
distilled water, Suprapur , Merck). Samples were pre-treated in
an ultrasound water bath for about 30 min at room temperature to homogenize the mixture. Each sample was then heated at
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
in Vitis vinifera L. cv. “Glera”. Chemie Erde - Geochemistry (2017), http://dx.doi.org/10.1016/j.chemer.2017.01.003
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Table 2
Median concentrations of elements in juice residue of grapes from “Glera” vineyards, analyzed by ICP-MS. The values are expressed in ppm (g/g) from B to Zn, and in ppb
(g/kg) from Ag to Zr. All abbreviations as in Table 1.
ppm
Aleandri
N=9
Bottazzo
N=9
Gaiarine
N=9
Nardin
N=9
Pattarello
N=9
p-value
B
Ca
Cu
Fe
K
Mg
Mn
Na
Rb
Zn
2.26 ± 0.7
62.2 ± 13.9
1.10 ± 0.32
0.72 ± 0.4
1892 ± 753
59.4 ± 17.3
0.29 ± 0.1
4.75 ± 1.8
1.89 ± 1.1
0.37 ± 0.03
2.73 ± 0.2
69.9 ± 15.9
0.87 ± 0.5
0.77 ± 0.02
1325 ± 329
52.7 ± 12.4
0.45 ± 0.21
2.89 ± 1.46
1.49 ± 0.05
0.30 ± 0.05
1.36 ± 0.2
92.1 ± 19
1.44 ± 1.1
0.55 ± 0.3
1689 ± 336
46.4 ± 12
0.31 ± 0.05
3.41 ± 1.0
0.73 ± 0.2
0.33 ± 0.01
2.73 ± 0.03
45.3 ± 6.8
0.64 ± 0.18
1.12 ± 0.4
1834 ± 251
58.9 ± 8.4
0.28 ± 0.07
3.55 ± 0.5
0.56 ± 0.4
0.27 ± 0.1
2.66 ± 0.54
57.4 ± 9.3
2.16 ± 0.7
1.32 ± 0.4
1704 ± 78.9
59.7 ± 8.72
0.38 ± 0.09
4.24 ± 1.3
1.25 ± 0.3
0.24 ± 0.1
***
***
*
n.s
n.s
n.s
n.s
n.s
*
n.s
Ag
Al
As
Ba
Co
Cr
Ga
Mo
Ni
Pb
Sr
Y
Zr
0.38 ± 0.11
248 ± 50.4
16.0 ± 8.1
27.4 ± 12.3
1.45 ± 0.8
2.90 ± 0.9
3.13 ± 1.3
5.48 ± 1.0
6.18 ± 4.3
2.00 ± 0.84
113 ± 30
0.17 ± 0.10
1.05 ± 0.40
0.48 ± 0.11
267 ± 90.3
19.8 ± 9.6
21.3 ± 7.9
1.78 ± 0.21
0.75 ± 0.4
1.26 ± 0.8
3.99 ± 1.1
11.1 ± 4.3
3.25 ± 1.5
107 ± 25
0.15 ± 0.05
0.75 ± 0.06
0.18 ± 0.09
245 ± 66
22.0 ± 8.0
34.3 ± 7.2
2.43 ± 0.5
1.37 ± 0.4
1.80 ± 1.0
11.6 ± 3.8
13.5 ± 8.8
0.91 ± 0.6
95.6 ± 21
0.15 ± 0.03
0.64 ± 0.1
0.20 ± 0.1
83.1 ± 27
10.9 ± 6.9
15.3 ± 2.1
2.06 ± 0.3
0.73 ± 0.4
1.14 ± 0.4
12.2 ± 5.2
9.48 ± 5.8
1.23 ± 0.2
80.3 ± 3.4
0.17 ± 0.09
0.64 ± 0.4
0.55 ± 0.13
311 ± 71
15.5 ± 12
29.2 ± 3.4
2.89 ± 0.9
3.48 ± 0.9
1.26 ± 0.9
3.62 ± 1.2
20.4 ± 9.3
1.22 ± 0.53
81.2 ± 6.6
0.26 ± 0.08
0.78 ± 0.08
**
***
n.s
***
*
*
n.s
n.s
n.s
*
***
*
***
Table 3
Median concentrations of elements in solid residue of grapes from “Glera” vineyards, analyzed by ICP-MS. The values are expressed in ppm (g/g) from B to Zn, and in ppb
(g/kg) from Ag to Zr. All abbreviations as in Table 1.
ppm
Aleandri
n=9
Bottazzo
n=9
Gaiarine
n=9
Nardin
n=9
Pattarello
n=9
p-value
B
Ca
Cu
Fe
K
Mg
Mn
Na
Rb
Zn
4.41 ± 0.2
450 ± 65
4.92 ± 0.3
4.81 ± 0.4
2071 ± 88
141 ± 9.4
2.36 ± 0.4
2.79 ± 1.1
3.80 ± 1.8
1.68 ± 0.1
4.55 ± 0.8
407 ± 39
4.39 ± 0.2
3.40 ± 0.9
2466 ± 387
112 ± 29
1.28 ± 0.6
4.39 ± 1.2
3.12 ± 0.5
0.92 ± 0.2
2.73 ± 0.4
331 ± 112
5.17 ± 0.4
5.75 ± 0.9
3174 ± 869
67.4 ± 15
0.77 ± 0.3
2.42 ± 1.1
1.35 ± 0.6
1.03 ± 0.34
3.86 ± 0.8
212 ± 107
1.76 ± 0.7
3.72 ± 1.1
3368 ± 1103
91.3 ± 28
0.75 ± 0.2
3.06 ± 0.3
1.26 ± 0.3
0.58 ± 0.2
4.48 ± 1.4
177 ± 72
8.54 ± 2.9
7.13 ± 1.1
3326 ± 488
60.5 ± 17
1.14 ± 0.5
3.66 ± 0.6
3.08 ± 1.0
0.68 ± 0.2
**
***
n.s
n.s
n.s
***
***
n.s
*
***
Ag
Al
As
Ba
Co
Cr
Ga
Mo
Ni
Pb
Sr
Y
Zr
1.50 ± 0.3
364 ± 64
16.8 ± 3.1
334 ± 49
6.92 ± 2.3
8.12 ± 7.1
10.1 ± 8.9
20.8 ± 2.4
52.4 ± 2.9
5.31 ± 1.3
994 ± 130
0.30 ± 2.0
2.99 ± 0.6
2.00 ± 0.3
533 ± 57
15.3 ± 7.3
172.1 ± 15
4.83 ± 1.3
2.69 ± 1.9
5.16 ± 3.4
9.68 ± 3.6
56.9 ± 9.7
2.95 ± 0.7
676 ± 64
1.14 ± 0.5
2.94 ± 0.9
1.56 ± 0.87
126 ± 19
25.0 ± 4.6
304 ± 105
6.00 ± 1.2
7.81 ± 4.5
9.00 ± 4.1
17.2 ± 9.4
15.2 ± 3.7
0.90 ± 0.6
918 ± 103
0.17 ± 0.07
2.32 ± 1.0
0.71 ± 0.2
219 ± 81
14.5 ± 1.9
134 ± 31
5.00 ± 1.7
5.15 ± 1.5
4.23 ± 1.8
1.69 ± 0.4
33.5 ± 4.9
2.28 ± 0.6
670 ± 138
0.16 ± 0.1
0.74 ± 0.2
2.36 ± 1.0
616 ± 140
13.9 ± 6.3
355 ± 65
4.64 ± 1.6
4.65 ± 1.4
9.87 ± 3.3
12.8 ± 4.5
20.5 ± 2.4
4.92 ± 1.1
927 ± 125
0.36 ± 0.1
2.21 ± 1.0
**
***
n.s
***
n.s
n.s
n.s
***
***
n.s
***
**
***
110–140 ◦ C for 3 h until complete drying and resuspended in 2 mL
HNO3 .
An amount of 2.5 g of SR was accurately weighed in the Teflon
vessel, adding 4 mL HNO3 and 3 mL H2 O2 . Samples were pre-treated
in an ultrasound water bath for 1 h at room temperature, heated
at about 180 ◦ C for 4 h until complete drying and resuspended
in 3 mL HNO3 . All JR and SR samples were transferred in plastic
(Perfluoroalkoxy-copolymer, PFA) flasks and made up to 100 mL
®
with highly purified Milli-Q water. As a control and for correction of instrumental drift, an internal Rh-Re standard was added to
each sample to a final concentration of 10 ppb and all samples were
analysed by inductively coupled plasma-mass spectrometry (ICP-
MS) using a Thermo Electron Corporation X series spectrometer
(Thermo Fisher Scientific, Waltham, Massachusetts).
2.3. Analytical determinations
The determination of major and trace elements in soils was
performed by X-ray fluorescence, using a wavelength dispersive
spectrometer ARL ADVANT’XP (Thermo Fisher Scientific, Waltham,
Massachusetts). The chemical composition of soils was expressed
as a weight percentage of the following oxides (SiO2 , TiO2 , Al2 O3 ,
Fe2 O3 , MnO, MgO, CaO, Na2 O, K2 O, P2 O5 ) and as ppm for the
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following trace elements: Ba, Co, Cr, La, Nb, Ni, Pb, Rb, Sr, V, Y, Zn,
Zr, Cu, Ga, Nd and Sc.
Accuracy was generally lower than 2% for major oxides and less
than 5% for trace elements determinations: the detection limits
for major oxides were 0.03–0.05% and for trace elements 1–2 ppm
(Lachance and Trail, 1966; Saccani et al., 2014).
The chemical elements in JR and SR were determined by inductively coupled plasma-mass spectrometry (ICP-MS) using a Thermo
Electron Corporation X series spectrometer (Thermo Fisher Scientific, Waltham, Massachusetts). The elements determined were Al,
Ag, B, Ba, Ca, Co, Cr, Cu, Fe, Ga, K, Mg, Mn, Mo, Na, Ni, Pb, Rb, Sr, Zn,
Y and Zr. Accuracy was generally lower than 15% for all elements.
The detection limits were 1–10 ppb for Al, Ca and Fe, 0.1–1 for Mg,
K and Na, and less than 0.1 ppb for all other elements.
The accuracy of the analysis of soil samples was checked by
NIST 2709 and USGS GXR-2 certified reference materials. The stan-
dard reference materials for ICP-MS were SRM 1547–Peach Leaves
and SRM 1567a – Wheat Flour (National Institute of Standards and
Technology, Gaithersburg, Maryland).
2.4. Statistical analysis
The Kruskal-Wallis non-parametric test (with post-hoc Dunn’s
test) was employed to establish the differences among groups
in all data from soil, and from JR and SR samples. Linear discriminant analysis (LDA) was found to be the most appropriate
multivariate statistical technique for the interpretation of all data.
In this technique the user must assign a classification group to all
sample data: the differences among these predetermined groups
describe combinations of variables (Rencher, 2002). The variables
were evaluated by means of stepwise LDA, using a Wilks Lambda
test (p-value < 0.01) and an F-statistic factor (Rencher, 2002). All
Fig. 4. Linear regression values of concentrations of Cu (a), Rb (b) and Sr (c) in juice residue (JR) vs solid residue (SR), showing a significant correlation (R2 > 0.60) with an
internal and external 95% confidence interval. Values of trace elements are expressed in g/g.
Fig. 5. Average values and standard deviation of concentrations of Sr in soil vs JR (a) and SR (b) in the five vineyards studied. Linear regression and confidence intervals as in
Fig. 4. Values of Sr are expressed in g/g.
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data analyses were carried out by the software XLSTAT (Version
2015.5.02, Addinsoft, Paris, France).
3. Results and discussion
3.1. Soil characterization by XRF analyses
Table 1 reports the chemical composition of collected soil
samples from each vineyard. Statistically significant differences
(p < 0.05) were obtained for most values of major and trace elements. The highest concentration value for major elements and for
all vineyards was SiO2 , followed by Al2 O3 , Fe2 O3 , MgO and CaO.
Examining the differences in oxide concentrations among vineyards, CaO resulted much higher in Aleandri and Bottazzo vineyards
in comparison to Pattarello, Gaiarine and Nardin. Concerning trace
elements, the highest concentration was Ba, followed by Sr, Rb and
Zr. The highest concentrations of Cr were detected in vineyards
Nardin and Gaiarine, and those of Zr in Pattarello and Gaiarine.
Generally, the concentrations values of major and trace elements
apparently changed according to geographical origin of soils.
The bivariate plots of concentrations of major element oxides
in Table 1 are shown in Fig. 2. The comparison between Al2 O3
and SiO2 (Fig. 2a) suggests a higher concentration of quartz minerals in vineyards Nardin, Gaiarine and Pattarello, and a lower one
in Aleandri and Bottazzo, confirming previous results obtained by
X-ray powder diffraction (XRD) by Petrini et al. (2014). Comparing CaO and SiO2 (Fig. 2b), a higher concentration of calcite and
dolomite is detected in vineyards Aleandri and Bottazzo, according
to previous data obtained by XRD (Petrini et al., 2014). The higher
values of Al2 O3 vs Fe2 O3 detected in vineyards Nardin, Gaiarine
and Pattarello are probably due to clay minerals and Al/Fe hydrous
oxides present in alluvial deposits (Fig. 2c).
The bivariate plots of concentrations of trace elements are
shown in Fig. 3. The values of Al2 O3 vs Rb, Zr, and Cr are respectively shown in Fig. 3a–c, and those of TiO2 vs Zr in Fig. 3d. In all
vineyards the values of Al2 O3 vs Rb supports the presence of clays
minerals, related to high content of aluminosilicates in soil fine
sediments (Fig. 3a). The correlation Al2 O3 vs Zr (Fig. 3b) higher in
Nardin and Gaiarine vineyards suggests the presence of sialic minerals and their residues, related to Zr-rich sediments. The presence
7
of metal-rich phyllosilicates in all vineyards, with higher values in
Nardin, Gaiarine and Pattarello, revealed by values of Al2 O3 vs Cr
(Fig. 3c), suggests the presence of chlorite in soil sediments, as previously reported for Po River Delta (Di Giuseppe et al., 2014). The
values of TiO2 vs Zr (Fig. 3d) follow the same pattern of Al2 O3 vs Cr
and suggest the presence of Ti-rich complex silicates. The Ti to Zr
ratio could be used to identify the soil origin (Hutton, 1977; Ishiga
et al., 2013; Schaetzl and Anderson, 2005).
Generally, all vineyard soils showed a heterogenous siliciclastic
and carbonate composition whose distribution changed according
to geographic origin. The high values of Ti, Zr and Cr support a high
degree of weathering of all soils examined (Schaetzl and Anderson,
2005). In addition, the data in Fig. 3c and d indicate that Cr and Zr
can be used as discriminatory elements for geographical origin of
the examined soils.
3.2. Major and trace elements in grape berries and soil
Chemical compositions of juice residue (JR) and solid residue
(SR) of grape berries collected in the five vineyards are respectively
reported in Tables 2 and 3. According to the results shown in the
two tables, the concentration values of all elements are higher in SR
than in JR, supporting previous data obtained with slightly different
protocols (Teissedre et al., 1994; Rogiers et al., 2006; Bertoldi et al.,
2009, 2011; Young et al., 2010).
In JR there was a slight prevalence of statistically significant differences (p < 0.05) in element concentrations (Table 2). The highest
values of major elements in JR (Table 2) were respectively K, Ca,
Mg, and Na, but the only statistically difference among vineyards
was that of Ca. Concerning trace elements, the highest values were
respectively Rb, Al, Sr and Ba, and all these values had statistically
significant differences among vineyards.
In SR (Table 3) about two-thirds of values were statistically
significant (p < 0.05). The highest concentration values of major
elements in SR were K, Ca, Mg, B and Na: all were statistically significant except K and Na. For trace elements, the highest values were
respectively Sr, Rb, Al and Ba, all statistically significant.
The concentration values of all elements in JR were plotted
against those in SR and the linear regression values were calculated.
Only three elements (Cu, Rb and Sr) showed a significant correlation
Fig. 6. Linear discriminant analysis (LDA) plot of the values of element concentrations in soils of the five vineyards shown in Table 1. The factor loading plot is shown on the
right side: F1, first discriminant function; F2, second discriminant function.
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
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(R2 > 0.60) with an internal and external 95% confidence interval
(Fig. 4). The highest correlation was that of Cu, probably related
to agronomic practices (Vitanović et al., 2008; Volpe et al., 2009;
Fregoni and Viticoltura di Qualità, 2013; Vystavna et al., 2014).
For trace elements, the Rb values could be related to the interchangeability of this element with K, previously documented in
plants (Kabata-Pendias, 2011). The effect of Rb on plant growth and
the development may depend on its concentration and on relative
abundance of K and Na (El-Sheikh and Ulrich, 1970) Moreover, a
possible deficiency of available K in soils could be at least compensated by uptake of Rb (Tyler, 1997; Drobner and Tyler, 1998;
Kabata-Pendias, 2011).
Based on the above data, all JR and SR values of major and
trace elements were correlated to the respective element concentration in the soils of the five vineyards. The only element that
showed a signification correlation with soil concentration (respectively R2 > 0.76 in JR and R2 > 0.60 in SR) was Sr (Fig. 5). It is known
that Sr is interchangeable with Ca according to the plant metabolic
requirements: its uptake may be increased by Ca and probably by
Mg, and decreased by K and Na (Kabata-Pendias, 2004). Experimental data confirm that an increased level of Ca in the growth medium
stimulates Sr uptake by plants (Kabata-Pendias, 2011). Previously
obtained 87 Sr/86 Sr data for the same vineyards (Petrini et al., 2014)
support the hypothesis that the positive linear correlation detected
for Sr in the five vineyards is due to the Sr concentration in soil.
Fig. 7. Linear discriminant analysis (LDA) plot of the values of element concentrations in JR (a) and SR (b) of the five vineyards, respectively shown in Tables 2 and 3. The
factor loading plots are shown on the right side: F1, first discriminant function; F2, second discriminant function.
Please cite this article in press as: Pepi, S., et al., Relationship among geochemical elements in soil and grapes as terroir fingerprintings
in Vitis vinifera L. cv. “Glera”. Chemie Erde - Geochemistry (2017), http://dx.doi.org/10.1016/j.chemer.2017.01.003
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3.3. Multivariate analysis by LDA of major and trace elements
3.3.1. Soil
Stepwise linear discriminant analysis (LDA) using a Wilks
Lambda test (p-value < 0.01) and an F-statistic factor (Rencher,
2002) were applied to all data of major and trace elements in soils
from the five vineyards examined, by the software XLSTAT. Among
all functions calculated by the program, two were chosen as best
discriminating functions among all data sets (Rencher, 2002). Both
discriminating functions were associated to the values of major elements and trace elements shown in Table 1), and the plot of the
first discriminant function (F1) against that of the second one (F2)
is shown in Fig. 6. The LDA analysis is clearly able to discriminate
the soil samples according to their geographical origin, with a validation of 73.05%, confirming that it is possible to identify each one
of the five wineries (Fig. 6). The highest discrimination among soils
is linked to F1, in which the elements selected by the forward stepwise process for the discriminant plot are MgO, MnO, Na2 O, K2 O,
P2 O5 , Ba, Co, Cr, La, Nb, Sr, V, Zn, Zr.
3.3.2. Juice and solid residue
The LDA analysis was applied in the same conditions to the data
of juice residue (JR) (Fig. 7a) and solid residue SR (Fig. 7b), respectively shown in Tables 2 and 3. The two functions F1 and F2 were
selected as previously described (Rencher, 2002). The elements
selected by the forward stepwise process for the discriminant plot
were Ag, Al, B, Ba, Ca, Co, Rb, Sr, Zn, Zr in JR, and Al, B, Ba, Ca, Mg,
Mn, Ni, Sr, Zn, Zr in SR.
The LDA model yielded 93.33% of sample validation for JR
(Fig. 7a) and 97.78% for SR (Fig. 7b). According to F1 and F2, the
two different grape residues yielded separate groups for each winery, thus the LDA analysis was clearly able to discriminate all JR and
SR samples according to their geographical origin. The results in JR
and SR showed that the plants accumulate elements in different
parts depending on geochemical properties of the soils. These data
confirmed that each winery could be identified by its geographic
origin.
The LDA multivariate analysis enabled to successfully discriminate the geochemical composition (thus the geographical origin) of
soil and Glera grape berries from the five different wineries. Based
on this analysis, the elements useful as possible geochemical markers for provenance of Glera grape berries, in order of relevance, are
Sr, Ba, Ca, Mg, Al, K, Zn, B, Ni, Co.
4. Conclusions
Major and trace elements in soil and grape berries of “Glera”, a
Vitis vinifera cultivar from two Northern Italian Regions, were evaluated as possible geographical markers for territoriality of products
made in Italy. The analysis of soils yielded a geological characterization for each of the five wineries examined. The study reveal
the different concentrations of major and trace elements in juice
residue and solid residues of grape berries. This study provides a
new simplified protocol, based on geochemical markers, allowing
rapid identification of the geographical origin of grapes. Comparing
results on soil and on grape berries, the only element that provide
a clear geochemical correlation between soil and grape berries is
Sr. However, the LDA multivariate analysis allowed to detect geochemical correlations of other elements besides Sr, namely, Ba,
Ca, Mg, Al, K, Zn, B, Ni, and Co. All these elements could establish a reliable correspondence between the geolithological features
of the vineyard soil and the chemical composition of juice and
solid residues. Overall, besides combined element characteristics
assessed by LDA multivariate analysis, Sr turn out as key marker of
soil provenance for the geographical origin of the Glera grape.
9
The relationship between soil and grape berries confirm that
major and trace elements could act as geochemical markers of
Glera grapes according the geological area. These elements could be
also useful to establish geochemical fingerprintings for testing the
origin of Prosecco wine, in order to protect the Made in Italy trademarks against falsifications and fraudulent use of denomination
labels.
Acknowledgments
The authors owe thanks Renzo Tassinari for technical advice
and experimental support, Umberto Tessari for support in analyses,
and Salvatore Cavaleri for elaboration of the geological map. The
authors also wish to thank the personnel of the five Italian wineries “Aleandri”, “Bottazzo”, “Gaiarine”, “Nardin” and “Pattarello” for
help in collecting samples. This research was funded by the Italian
Ministry of Education, Universities and Research (doctoral fellowship MIUR-27-GEO09-2012), by the Veneto Region Agency for
Agriculture (Conegliano, Treviso, Italy) and by the Teknehub Laboratory (University of Ferrara, Ferrara, Italy). The authors are very
grateful to Prof. Martin Dietzel and Editor in Chief Alex Deutsch for
their careful and dedicated job of critical revision of the manuscript.
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