8E Identification of Impact Odorants of Wines 399
AEDA
Charm
AEDA
Charm
3.25 fruits
6.12 fusel
6.42 honey
R.T. Odor
Dilution 0 Dilution 1
R.T. Odor R.T. Odor
Dilution 2
3.26 fruits 3.25 something
6.42 sweet
15 Time (min)
3.25 6.12 6.42
Dilution 0
Dilution 1
Dilution 2
R^2 = 32 = 9
R^0 = 30 = 1
R^1 = 31 = 3
time
1
3
9
dilution
FD
Fig. 8E.1Scheme showing the basics of AEDA and Charm analysis. Different sequential dilutions
of the sample extract are analyzed in the GC-O system. In AEDA the judge simply marks the
retention times and the odor descriptions. The FD value is Rp, where p is the p-th dilution of
the extract at which the odor was last detected and R is the dilution rate (3 in the figure). In
Charm, he/she presses the space bar of the computer during the odor detection, and the outputs are
combined to form the Charm chromatogram
reproducible than Charm analysis (Debonneville et al., 2002) or some posterior
intensity methods (van Ruth, 2004). However, the dynamic range of the response
is narrower in the case of NIF and this means that in the practice it is easier to dis-
criminate concentration differences in posterior intensity methods (van Ruth, 2004).
8E.2.1.3 Techniques Based on the Measurement of Intensity
The first technique of this type was OSME (McDaniel et al. 1990; Miranda-Lopez
et al. 1992) which was introduced at the beginning of the 1990s. In this technique the
judge handles a knob connected to a variable resistance which is actuated following
the intensity of the odor eluting out of the column. That is, the judge acts as a gen-
uine GC detector. The output is something very similar to a chromatogram (aroma-
gram, odorgram or osmegram) in which the peaks are related to the intensity (peak
height) and intensity×time (peak area) of the odors presented in the sample. The
technique is really appealing; however, in its original form the task imposed on the
judges is extremely difficult and, consequently, the results are poorly reproducible
and difficult to handle. It should be considered that the judges require some time to
detect the odor, to estimate their intensity and to assess simultaneously its quality,
and that a continuous monitoring requires a continuous and systematic feedback
(da Silva et al. 1994). As a consequence, the technique has been simplified so that
the judges do not try to follow closely the odor intensity of the effluent, but rather
to detect the peak start and end and to provide an evaluation of the intensity. The
peaks, then, look like simple triangles instead of genuine chromatographic peaks.