2,4,6-Trichloroanisole (TCA) contamination of wine determines huge economic losses for the wine industry estimated to amount to several billion dollars yearly. Over 50 years of studies have determined that this problem is often caused by TCA contamination of the cork stopper, which releases TCA into the wine. The human threshold for TCA is extremely low. A wine contaminated by 1-2 ng/L TCA can be perceived as tainted. Contaminations with <0.5 ng/L TCA are commonly considered negligible and are not perceivable. The possibility of prescreening cork stoppers for TCA contamination would be an enormous advantage. Therefore, the demand for a fast, nondestructive method capable of quantifying the TCA contamination in cork stoppers is impelling. Vastly used analytical methods have so far struggled to provide a fast and reliable solution, whereas sensory analysis by trained panelists is expensive and time-consuming. Here we propose a novel approach based on chemical ionization-time-of-flight (CI-TOF) mass spectrometry employing the "Vocus" ion source and ion-molecule reactor. The technique proved capable of nondestructively quantifying TCA contamination in a single cork stopper in 3 s, with a limit of quantification below the perception threshold. A real test on the industrial scale, quantifying TCA contamination in more than 10000 cork stoppers in a few hours is presented, representing the largest data set of TCA analysis on cork stoppers within the literature and proving the possibility to apply the technique in an industrial environment. The correlation with standard methods for releasable TCA quantification is also discussed.
2,4,6-Trichloroanisole (TCA) contamination of wine determines huge economic losses for the wine industry estimated to amount to several billion dollars yearly. Over 50 years of studies have determined that this problem is often caused by TCA contamination of the cork stopper, which releases TCA into the wine. The human threshold for TCA is extremely low. A wine contaminated by 1-2 ng/L TCA can be perceived as tainted. Contaminations with <0.5 ng/L TCA are commonly considered negligible and are not perceivable. The possibility of prescreening cork stoppers for TCA contamination would be an enormous advantage. Therefore, the demand for a fast, nondestructive method capable of quantifying the TCA contamination in cork stoppers is impelling. Vastly used analytical methods have so far struggled to provide a fast and reliable solution, whereas sensory analysis by trained panelists is expensive and time-consuming. Here we propose a novel approach based on chemical ionization-time-of-flight (CI-TOF) mass spectrometry employing the "Vocus" ion source and ion-molecule reactor. The technique proved capable of nondestructively quantifying TCA contamination in a single cork stopper in 3 s, with a limit of quantification below the perception threshold. A real test on the industrial scale, quantifying TCA contamination in more than 10000 cork stoppers in a few hours is presented, representing the largest data set of TCA analysis on cork stoppers within the literature and proving the possibility to apply the technique in an industrial environment. The correlation with standard methods for releasable TCA quantification is also discussed.
Cork taint
in wine mainly caused
by 2,4,6-trichloroanisole (TCA) is a tremendous problem for the cork
and wine industry causing annual losses exceeding 10 billion dollars.[1] Despite wine being a complex matrix constituted
by hundreds of different aroma compounds, the presence of a few ng/L
of TCA may completely spoil the wine.[2] The
discovery of TCA as a compound responsible for cork taint in wine
dates back to the early 1980s.[3] Since then,
it has been established that TCA is responsible for the majority of
the wines spoiled by cork taint, but other compounds can also be possible
causes. For example, Chatonnet et al.[4] identified
2,4,6,-tribromoanisole (TBA) as causing musty or corked taint in wine
that did not contain significant levels of chloroanisoles, confirming
suggestions from earlier studies.[5] 2,4-dichloroanisole
(2,4-DCA), 2,6-dichloroanisole (2,6-DCA), 2,3,4,6-tetrachloroanisole
(TeCA), and pentachloroanisole (PCA) in the cork might also taint
the wine but their role is mostly minor.[2]Despite almost 30 years of investigations,[6−10] the ultimate reasons for the presence of TCA in wine
are not fully understood.[11] To date, only
TCA transferred from the cork stopper into the wine has been identified,
as experiments trying to demonstrate TCA formation from precursors
(trichlorophenols) in wine have shown that it is not the case.[12] The presence of TCA and other chloroanisoles
in the corkwood is still largely unknown as well as responsible microorganisms
and the timing of the formation.[11] Precursors
may originate from chlorophenolic biocides and be transformed into
chloroanisoles by several microorganisms.[13] Moreover, they may be formed from compounds naturally occurring
in wood or cork through chlorination and microbial methylation reactions.[13] It is common knowledge among cork producers
that the incidence of TCA is higher in unmanaged cork oak forests
with a strong presence of low vegetation than in managed forests subjected
to regular cleaning operations. Cork stoppers produced from the same
bark may be contaminated with highly variable levels of TCA since
its presence is strongly localized.[13] Therefore,
the level of contamination must be determined in single cork stoppers,
as TCA screening of the bark would either result in unnecessary cork
discards or would often overlook localized TCA contaminations.Prescott et al.[14] determined the consumer
rejection threshold and sensory detection threshold for TCA taint
in wine to be 3.1 and 2.1 ng/L, respectively. Later studies suggested
that the sensory detection threshold could be even lower, around 1
ng/L.[15] Therefore, TCA screening of single
cork stoppers at an industrial scale poses a serious analytical challenge.
A fast, sensitive, accurate, nondestructive analytical method is required
but at present, despite many attempts, a break-through in cork screening
at an industrial scale has not been realized. Since only a small part
of the TCA content of the cork stopper is able to migrate to the wine,[16−18] a common approach adopted by the cork and wine industries is the
analysis of releasable TCA.[2] Standards
of releasable TCA analysis are described by ISO 20752:2014 and by
the OIV organization.[20] Basically, a cork
stopper is subjected to a 24 h soaking in a wine-simulant (or, alternatively
in the OIV standard, in white wine) and the concentration of TCA is
determined (in ng/L) in the extracting solution by either SPME-GC-MS
or SPME-GC-ECD. The detection limits of such methods are typically
in the range 0.2–0.5 ng/L[21] and
therefore are suitable for the application. In contrary, sample preparation
time, analysis time, and sample destruction/modification make them
unsuitable for nondestructive industrial screenings and limit their
application solely to laboratory analyses (in industry quality control
laboratories and external laboratories).The methods for releasable
TCA analysis in cork stoppers have been
recently reviewed.[2,22,23] Traditional methods are typically based on gas chromatography after
extraction in a suitable solvent. Preconcentration is typically achieved
using stir bar sorptive extraction,[24] solid
phase extraction,[25] or, more often, solid
phase microextraction (SPME).[26] Detection
is then performed by Electron Capture Detector (ECD)[27] or by mass spectrometry.[26,28] Evolutions
of the technique introduced microwave assisted extraction over 2 h
in place of the 24 h soaking, thus, strongly decreasing the required
sample preparation time.[24] Biosensors have
also been proposed, employing specific TCA antibodies to analyze TCA
in about 5 min. They could detect TCA in cork soaks at concentrations
as low as 1.02 ng/L.[29,30] Since releasable TCA is considered
a destructive technique leading to surface modifications,[15] the industry is aiming for methods that are
nondestructive, fast, and correlate with releasable TCA. The most
promising approaches in this direction involve the analysis of gaseous
TCA released by a single cork stopper in a vial or other closed container
upon heating.[31−33] Strong technological investments by major cork producers
in direct GC analysis provided solutions claiming to screen single
cork stoppers in 20 s at releasable TCA levels not exceeding 0.5 ng/L2 but are still leading to controversial outcomes (e.g., Todorov
and Courtwatch[34]). Some studies introduced
chromatography-free techniques to tackle the problem. The potential
of spectrometric techniques based on ion mobility in this field has
been first proposed[35] and then subsequently
further studied.[36]A large role in
nondestructive industrial TCA screenings is played
by sensory analysis. Different approaches exist. The standard method[37] implies partial soaking in distilled water for
24–48 h, followed by sensory analysis. According to the so-called
dry soak approach, single cork stoppers are placed in a closed vial
with some drops of water for 24 h, and the headspace air is subsequently
tested by trained panelists.[15] Other common
practices within the industry include preheating of dry corks at 150
°C for 10 min before sensory analysis, preheating of maceration
vessels at 80 °C for 2 h, or the use of sparkling water instead
of distilled water for maceration. However, sensory approaches are
time-consuming and expensive.[2] Moreover,
the “sensory approaches” used today in the cork industry
are rather “sniff tests” focused on high capacity production
(typically 2000 corks/day/panelist), using a single trained panelist
per single sample, and are therefore subjective, lacking any of the
criterium of objectivity. Further, such approaches unavoidably lead
to sensory saturation and, therefore, to false negatives and positives,
as TCA is an olfactive suppressor agent.[38] In order to obtain objective results, the quantitative descriptive
analysis or flavor profile of any food or food-related single sample
should be estimated by means of a sensory team composed of 8–12
trained panelists,[39] and the repeatability
and the reproducibility of the sensory panel should be regularly and
continuously tested by the panel leader according to standard guidelines.[40] Objective sensory sessions are thus slow and
have a very low capacity.The present study is the first exploitation
of a novel method for
the online detection of TCA based on chemical ionization mass spectrometry
(CI-MS). This method omits the use of chromatography and recovers
the separation by high resolution mass spectrometry and by selective
and soft ionization. The CI source in CI-MS involves the production
of reagent ions in a dedicated reagent ion source. The reagent ions
are then transferred into an ion–molecule reactor (IMR) where
they encounter the analyte and produce the analyte ions by chemical
ionization. The instrument used here uses a discharge reagent ion
source and an IMR operated at a medium pressure of ≈1.5 mbar[41] coupled to time-of-flight mass spectrometry
(TOFMS). Krechmer et al.[42] recently described
the performance and the potential of the new instrument (Vocus 2R,
from Tofwerk, Switzerland) when used with proton transfer reaction
chemical ionization, showing a more than 10-fold sensitivity improvement
for volatile compound detection compared to current state-of-the art
instruments. Here, chemical ionization via electron transfer to NO+ reagent ions is employed to ionize TCA. The sampling from
gaseous cork emission is done without preconcentration or trapping.
The method, therefore, strongly resembles the sensory analysis mentioned
above, but using an artificial rather than a human nose.The
aim of the study is 3-fold. We first show that the Vocus can
detect TCA in natural cork stoppers at concentrations below the sensory
threshold in 3 s. The correlation with releasable TCA determinations
according to ISO 20752:2014[19] and OIV[20] is then investigated. Finally, a real industrial
scenario is simulated by determining TCA in 10100 natural cork stoppers
from three different batches in just 8 h and 25 min, corresponding
to 3 s per cork stopper.
Materials and Methods
Cork Stoppers
Natural cork stopper samples (24 mm diameter,
49 mm length) were obtained directly from several producers. Cork
visual grades ranged from Flor to II according to the international
guide.[43] All stoppers were not coated;
therefore, no material other than cork was present. Calibrations,
method testing, and comparison with other TCA analysis methods were
performed on natural cork stoppers from a mixed batch. The testing
in an industrial scenario was performed on a mixed batch (100 natural
cork stoppers) from different producers and on two homogeneous batches
each consisting of 5000 natural cork stoppers from the same producer.
Vocus Cork Analyzer (VCA)
The VCA (Tofwerk AG, Switzerland)
includes a Vocus 2R high resolution chemical ionization mass spectrometer
coupled to a cork autosampler. The Vocus 2R reaches a mass resolving
power of up to m/dm = 15000. The discharge reagent-ion source was
operated at ≈2 mbar and generated NO+ reagent ions
from synthetic air (Alphagaz 1 Air, Air Liquide). The IMR was operated
at 1.5 mbar and 150 °C. The ion transmission into the TOFMS was
optimized using radio frequency ion focusing.[42,44,45] TCA ions are produced with chemical ionization (CI) via charge transfer.
Fragmentation of the analyte ions was negligible at the selected setup.
The cork stopper autosampler consists of individual cork stopper cavities
to prevent cross contaminations. The cavity temperature was generally
set to 120 °C, unless otherwise stated. The Vocus Cork Analyzer
was set to measure for 2 s from each cavity drawing headspace air
at 1 slpm (= standard liters per minute) through a PTFE sampling line
(1/8 in. i.d.) heated at 120 °C.Simultaneously, synthetic
air was flushed into the cavity in order to replace the sampled headspace
gas. The settling time between cavities was 1 s, resulting in a total
cycle period of Δt = 3 s/cork stopper. A total
of 5 sccm (sccm = standard cubic centimeters per minute) of 10 μL/L
(ppmv = parts per million by volume) benzene, toluene, and xylene
in pure nitrogen from a standard cylinder (Carbagas, Switzerland)
was mixed into the sample flow in order to monitor the primary ion
stability. The signal intensity expressed in counts per second (cps)
of the spectral peaks at 209.940 Th (corresponding to C7H5Cl3O+, 1 Th = 1 Da/e), 211.937
Th (isotope of C7H5Cl3O+), and 213.934 Th (isotope of C7H5Cl3O+) were summed and used as signal for TCA. The benzene
signal C6H6+ was used as an internal
standard in order to correct for possible sensitivity drifts. The
conversion into equivalent releasable TCA expressed in ng/L was carried
out upon calibration against the standard method (see next sections).
Releasable TCA Analysis According to Standard Methods
Releasable
TCA in natural cork stoppers was determined as described
in OIV-MA-AS315-16.[20] The used methodology
is also in accordance to ISO 20752:2014[19] with a minor modification; that is, the only deviation from the
ISO 20752:2014[19] prescriptions was the
fact that we avoided rounding the results to the “nearest 0.5”,
which is actually not in the provisions of the OIV method. The procedure
was as follows. A single cork stopper was placed into a 50 mL aqueous-alcoholic
solution (12% v/v alcoholic strength) for 24 h. In the case of cork
granules, 40 g of granules were placed in a 2 L flask and completely
covered with the aqueous-alcoholic solution, soaking for 24 h. A total
of 10 mL of solution was inserted into a 20 mL vial, adding 3 g of
NaCl and 100 mL of internal standard solution consisting of 10 ng/L
2,4,6-trichloroanisole-d5 (TCA-d5) in
an aqueous-alcoholic solution, 12% v/v. The vial was kept under stirring
at 35 °C. Headspace volatile compounds were collected for 15
min by a 2 cm Solid Phase Microextration fiber coated with divinylbenzene/carboxen/polydimethylsiloxane
50/30 μm (DBV/CAR/PDMS, Sigma-Adrich, St. Louis, U.S.A.). Volatile
compounds adsorbed on the SPME fiber were desorbed at 260 °C
for 2 min in splitless mode in the injector port of a GC interfaced
with a mass detector (GC Agilent 7820A with Agilent 5977B MSD, Agilent
Technologies, Santa Clara CA, U.S.A.). Separation was achieved on
an Agilent HP-5 capillary column (30 m × 0.25 mm ID × 0.25
μm film thickness; Sigma-Adrich, St. Louis, U.S.A.).The
GC oven temperature program consisted of 35 °C for 6 min, then
35–280 °C at 15 °C min–1, and stable
at 280 °C for 5 min. Helium was used as the carrier gas with
a constant column flow rate of 1 mL min–1. The mass
detector was operated in electron ionization mode (EI, internal ionization
source; 70 eV) in single ion mode. 195 Th, 210 Th, and 212 Th were
used to detect TCA and 199 Th, 215 Th, and 217 Th were used to detect
TCA-d5. 195 Th and 215 Th were employed for quantification of TCA
and TCA-d5, respectively. All reagents were purchased from Sigma-Aldrich
(St. Louis, U.S.A.). The used method is widely employed within the
cork industry and by accredited laboratories offering releasable TCA
analysis in cork stoppers. It is, therefore, of utmost importance
within the cork and wine sectors, as it is also employed (also in
court) to demonstrate that the stopper of a TCA-tainted wine bottle
is contaminated by TCA. In the following, the used method will be
generally referred to as “ISO”.
Results and Discussion
TCA Determination
in Natural Cork Stoppers with Vocus
Figure reports exemplificative
spectra of natural cork stoppers measured by the presented methodology.
The first cork stopper (Figure a) was determined to have 0.5 ng/L of releasable TCA using
the ISO method. This value is lower than the human sensory threshold
for TCA.[14,15] The second cork stopper (Figure b) was measured to have 1.6
ng/L of releasable TCA, which is close to the sensory threshold. In
both cases and despite the short analysis time of 3 s, both spectra
show a clear presence of TCA-related peaks at 209.940 Th (corresponding
to a positively charged molecule of TCA, C7H5Cl3O+) and at 211.937 Th and 213.934 Th corresponding
to the isotopes of TCAC7H5Cl237ClO+ and C7H5Cl37Cl2O+ respectively.
Figure 1
Excerpt of Vocus-measured
mass spectra (red) of two natural cork
stoppers. The upper spectrum corresponds to a natural cork stopper
determined to have 0.5 ng/L releasable TCA, according to OIV-MA-AS315-16.[20] The bottom spectrum corresponds to cork stopper
tainted with 1.6 ng/L of releasable TCA. In blue is the theoretical
isotopic distribution of TCA for comparison.
Excerpt of Vocus-measured
mass spectra (red) of two natural cork
stoppers. The upper spectrum corresponds to a natural cork stopper
determined to have 0.5 ng/L releasable TCA, according to OIV-MA-AS315-16.[20] The bottom spectrum corresponds to cork stopper
tainted with 1.6 ng/L of releasable TCA. In blue is the theoretical
isotopic distribution of TCA for comparison.A Vocus spectrum of a pure TCA standard (Sigma-Adrich, St. Louis,
U.S.A.) is shown in Supporting Information, Figure S1, together with the theoretical isotopic pattern showing
a very good agreement. Fragmentation of TCA-related parent ions was
determined to be <5%; thus, only the above-mentioned three major
parent ions were considered. In principle, a limitation of the proposed
method would be the fact that isomers of TCA would be superimposed
on the same exact masses, and the method would measure the sum of
all isomers. However, no isomers of TCA have been reported in natural
cork so far, to the best of our knowledge. Some TCA isomers (for example,
2,3,6-TCA) are suggested as possible internal standards[20] due to their absence in natural cork. Repeatability
of the measurements for three natural cork stoppers preheated at 120
°C is reported in Figure . Relative standard deviations are 2.7%, 4.2%, and 12% for
the three corks having releasable TCA of 10, 2.6, and 0.5 ng/L, respectively.
Linearity of the Vocus covers six orders of magnitude, which has been
demonstrated elsewhere;[42] here, it is relevant
to assess linearity of TCA determinations by Vocus within the actual
matrix (natural cork) and within the relevant range for cork screening.
Since the ISO methodology used to determine the amount of releasable
TCA in natural cork stoppers is affected by the uncertainty in the
step of soaking the cork stopper in a wine simulant solution (see
next section), linearity of the present method was first assessed
on cork granules (ca. 1 mm diameter) previously characterized by ISO. Figure exemplifies the
good linearity (R2 = 0.998) of the Vocus
in the relevant range of 0.5–10 ng/L.
Figure 2
Repeatability of Vocus
for TCA assessment of three natural cork
stoppers having different values of releasable TCA and preheated at
120 °C.
Figure 3
Example of linearity of the Vocus TCA signal
for cork granules
vs releasable TCA determined using SPME-GC-MS, as described in OIV-MA-AS315-16.[20] The dotted line represents a linear fit (R2 = 0.998).
Repeatability of Vocus
for TCA assessment of three natural cork
stoppers having different values of releasable TCA and preheated at
120 °C.Example of linearity of the Vocus TCA signal
for cork granules
vs releasable TCA determined using SPME-GC-MS, as described in OIV-MA-AS315-16.[20] The dotted line represents a linear fit (R2 = 0.998).From the characteristics of the instrument,[42] it can be calculated that the linearity range would extend
to about 5000 ng/L of releasable TCA.The next section reports
the correlation of Vocus and ISO for releasable
TCA determination on natural cork stoppers.The limit of detection
was determined to be 0.05 ng/L by repeatedly
(12 times) measuring 10 natural cork stoppers preheated at 120 °C
for which the TCA signal was at background level and therefore considered
as TCA-free samples (Table S1). The LOD
was estimated as 3× the standard deviation of the repeated measurement
of each cork, divided by the sensitivity. Compared to other methods
available in the literature, the LOD of the present methodology is
comparable or better,[2,21−23] with the advantage
being that it is achieved in just a 3 s cycle period. The sensitivity
of the method depends very much on the cork stopper preheating temperature. Figure reports the ratios
between the sensitivities at different preheating temperatures (90,
100, and 110 °C) and the sensitivity at 120 °C. Switching
the preheating temperature from 120 to 90 °C, the sensitivity
drops to less than 20%. In a first approximation, the behavior of
such a ratio can be explained by the change in saturation vapor pressure
of TCA. The saturation vapor pressures (Psat) of TCA for selected temperatures were calculated via the Clausius–Clapeyron
relationship. The enthalpy of vaporization (ΔHvap) for TCA was determined as ∼60 kJ/mol based
on tabulated values of Psat of TCA at
20 °C (3.066 Pa) and its boiling point of 241 °C.[46]
Figure 4
Dependence of TCA sensitivity on the natural cork stopper
preheating
temperature (blue). The theoretical dependence of TCA saturation vapor
pressure on temperature is also reported (red). Data are normalized
by the corresponding values at 120 °C.
Dependence of TCA sensitivity on the natural cork stopper
preheating
temperature (blue). The theoretical dependence of TCA saturation vapor
pressure on temperature is also reported (red). Data are normalized
by the corresponding values at 120 °C.
Comparison with ISO 20752:2014[19] and
OIV[20]
A set of 671 natural cork
stoppers was tested with the present method and by ISO. Figure reports the correlation between
Vocus and ISO for such data sets. R2 values
of the linear fit are 0.92, implying a Pearson correlation coefficient
of 0.96. The correlation is statistically significant (p < 0.01). In order to better evaluate such correlation results
and to have a benchmark, a set of cork stoppers was measured twice
according to ISO (Figure ), waiting a period of 15–30 days between measurements.
The R2 of the best fitting line is 0.68,
and the Pearson correlation is thus 0.82 (p <
0.01). Such values suggest that the correlation between Vocus and
ISO is limited by the precision of ISO. Considering the results obtained
with cork granules (see Figure ) and the good precision of ISO when measuring standard TCA
solutions or cork soaks,[21] the uncertainty
is likely derived from the sample preparation step, that is, the soaking
step. In such step each natural cork stopper is subjected to soaking
for 24 ± 2 h in a wine simulant solution. By eliminating the
soaking step, Vocus has the advantage of reducing the uncertainty
related to this step.
Figure 5
Comparison between releasable TCA determined using SPME-GC-MS,
as described in OIV-MA-AS315-16,[20] and
by Vocus on a set of natural cork stoppers.
Figure 6
Replicate
measurements of a set of 74 natural cork stoppers according
to OIV-MA-AS315-16.[20] All measurements
have been carried out waiting 15–30 days before the replicated
analysis.
Comparison between releasable TCA determined using SPME-GC-MS,
as described in OIV-MA-AS315-16,[20] and
by Vocus on a set of natural cork stoppers.Replicate
measurements of a set of 74 natural cork stoppers according
to OIV-MA-AS315-16.[20] All measurements
have been carried out waiting 15–30 days before the replicated
analysis.
Application to an Industrial
Scenario
Given the extremely
short measurement time for single cork stoppers, three sets of natural
cork stoppers from different producers were measured, for a total
of 10100 natural cork stoppers. The results for the smallest set,
consisting of 100 natural cork stoppers, are reported in Figure . The cork stoppers
were measured sequentially one after the other, and remarkably, the
total measurement time for the whole experiment was 5 min. This batch
included several cork stoppers that were highly contaminated with
TCA as well as cork stoppers having only a slight contamination, and
some cork stoppers showed a TCA signal below the detection limit. Figure summarizes the TCA
quantification in two different batches, each consisting of 5000 cork
stoppers. The total measurement time for each batch was 4 h and 10
min. For comparison, if the same experiment was carried out employing
the ISO method, it would have required more than four months of constant
analysis.
Figure 7
Example of an analysis of 100 natural cork stoppers measured by
Vocus. The measurement time was set to 2 s per stopper, and 1 s was
required to switch to the next stopper. Therefore, the total analysis
time for 100 stoppers was 300 s. Stoppers tainted by TCA levels differing
by several orders of magnitude were processed.
Figure 8
Example
of TCA analysis results of two natural cork stopper batches
(from two different producers) measured by VCA. Each batch consisted
of 5000 natural cork stoppers having the same dimensions. The total
analysis time for each batch has been 250 min. Histograms have been
generated using bins of 0.1 ng/L.
Example of an analysis of 100 natural cork stoppers measured by
Vocus. The measurement time was set to 2 s per stopper, and 1 s was
required to switch to the next stopper. Therefore, the total analysis
time for 100 stoppers was 300 s. Stoppers tainted by TCA levels differing
by several orders of magnitude were processed.Example
of TCA analysis results of two natural cork stopper batches
(from two different producers) measured by VCA. Each batch consisted
of 5000 natural cork stoppers having the same dimensions. The total
analysis time for each batch has been 250 min. Histograms have been
generated using bins of 0.1 ng/L.Moreover, the present method is nondestructive, and no visual damage
or deformation appeared on the cork stoppers (Tables S2–S4 and Figure S2). Therefore, the samples
can still be used (and, e.g., sold) after the analysis, provided a
remoisturizing step is carried out in order to restore the moisture
content. The latter procedure is very common within the cork industry.
The histograms reported in Figure indicate that the first batch is characterized by
an average lower TCA content than the second batch. Over 99% of the
cork stoppers were contaminated with <1 ng/L TCA and about 50%
with <0.5 ng/L TCA, which is presently considered a limit for TCA-free
corks within the cork industry.On the contrary, the second
batch had only a negligible percentage
of TCA-free corks, while almost all of them were contaminated with
>1 ng/L TCA.The present technique can be useful in an industrial
scenario to
screen natural cork stoppers based on their TCA contamination level
before they are sold or in a quality control laboratory in order to
quickly assess the TCA incidence in cork batches.
Conclusions
A novel nondestructive technique for quantification of the TCA
contamination in single cork stoppers has been presented. The approach
by far exceeds the performances of existing analytical methods in
terms of speed while having comparable detection limits for TCA. It
correlates with releasable TCA quantification using standard methods.
The new technique possesses the potential to be a breakthrough for
the cork and wine sector, providing the possibility of fast (3 s),
single cork stopper preselection based on the rapid quantification
of TCA contamination. Future developments include the investigation
of other cork contaminants, which are simultaneously detected by the
same technique.