For the
quantification of binary mixtures, neural networks were trained by the calibration
data and subsequently predicted the independent test data. The root mean square
errors (RMSE) of the test data and the crossvalidated calibration data measured
with the 6-sensor array setup are listed in the first row of table
1. The RMSE of the prediction of the R134a concentrations is about three
times higher than the RMSE of R22, whereby the relative RMSE of the test data
are 3.5% for R22 and 13.0% for R134a. The RMSE of the test data of both analytes
are only slightly higher than the RMSE of the crossvalidation of the calibration
data indicating good calibration models [79]. The predictions
of the test data are graphically shown in the true-predicted plots in figure
9. Thereby the predicted concentrations of the test data are plotted versus
the true known concentrations. Ideal predictions are consequently located on
the diagonal. As the single predictions cannot be graphically resolved, the
predictions of each concentration level are represented by the mean and the
standard deviation. It is visible that the predictions of both analytes are
not biased as the means of all concentration levels do not significantly deviate
from the diagonal. The smaller standard deviations of the plot of R22 show that
the predictions of the concentrations of R22 are more precise than the predictions
of R134a. Both, the RMSE and the true predicted plots allow the conclusion that
both, R22 and R134a, can be quantitatively determined in binary mixtures using
the RIfS array setup. Especially the more important detection of the harmful
R22 has proven to be very accurate over the whole concentration range.
figure 9: Predicted concentrations
versus true concentrations of the test data measured by the array setup.
figure 10: Predicted concentrations
versus true concentrations of the test data measured by the 4l setup.
The RMSE
for the measurements performed by the 2-sensor 4l setup are listed
in the second row of table 1, whereby the relative
RMSE of the test data are 7.4% for R22 and 21.4% for R134a. The RMSE of the
calibration data and the test data are also not significantly different indicating
again the absence of typical problems of calibrations by neural networks like
overtraining effects. Yet, the RMSE of both analytes are nearly twice as high
as the RMSE of the measurements performed by the array setup with 6 sensors.
The true-predicted plots in figure 10 correspond
with this higher RMSE. The high standard deviations of the true-predicted plot
of R134a show that the predictions are rather scattered. Additionally, the predictions
of the low concentrations are a little biased with the absence of R134a being
predicted as a relative saturation pressure of 0.0086 on average. On the other
hand, the true-predicted plot of R22 shows that the predictions of R22 are not
biased and more precise than the predictions of R134a demonstrating that a quantification
of R22 in the presence of R134a is possible by using the low-cost 4l setup.
The deterioration
of the quantification of both analytes using the 4l setup instead of
the array setup raises the question, if this deterioration is caused by the
reduction of the number of sensors or by the type of setup. Therefore, the data
set recorded with the array setup was calibrated with neural networks again,
but this time only the sensors PUT and UE2010 15% were used as input variables.
For the comparison the UE 2010 15% layer is used instead of the 20%
layer, as the UE 2010 layer used in the 4l setup is more similar to the UE 2010 15%
layer in respect to the thickness of the layer. The RMSE of this experiment
are listed in row 3 of table 1. The RMSE of R22
is nearly equal for the 4l setup and for the
array setup with 2 sensors. Thus, the deterioration of the prediction of R22
can be primarily ascribed to the limitation of the number of sensors. On the
other side, the RMSE of R134a of the 2-sensor array lies in between the 4l setup and the 6-sensor
array. Hence, not only the limitation of the number of sensors, but also the
type of setup plays a role for the quantification of R134a.
Setup
Crossv.
R22
Crossv.
R134a
Test
R22
Test
R134a
Test
Mean
Array: 6 Sensors
0.00162
0.00572
0.00183
0.00630
0.00406
4l: 2 Sensors
0.00325
0.01169
0.00317
0.01146
0.00732
Array: PUT + UE 2010 15%
0.00283
0.00750
0.00334
0.00891
0.00612
Array: PUT + UE 2010 20%
0.00182
0.00626
0.00203
0.00678
0.00440
Array: PDMS + UE 2010 20%
0.00184
0.00596
0.00206
0.00667
0.00436
Array: PDMS + M 2400
0.00238
0.00673
0.00268
0.00772
0.00520
Array: PDMS + UE 2010 15%
0.00276
0.00656
0.00329
0.00810
0.00569
Array: PUT + M 2400
0.00241
0.00776
0.00273
0.00881
0.00577
Array: PUT + PDMS
0.00611
0.01156
0.00685
0.01259
0.00972
Array: HBP + PDMS
0.0613
0.01122
0.00714
0.01257
0.00986
Array: HBP + UE 2010 20%
0.00177
0.01902
0.00199
0.02139
0.01169
Array: HBP + PUT
0.00657
0.01531
0.00773
0.01789
0.01281
Array: M 2400 + UE 2010 20%
0.00182
0.02371
0.00211
0.02371
0.01291
Array: HBP + UE 2010 15%
0.00316
0.02368
0.00384
0.02828
0.01606
Array: M 2400 + HBP
0.00320
0.02447
0.00393
0.02930
0.01661
Array: M 2400 + UE 2010 15%
0.00296
0.02774
0.00368
0.03436
0.01902
Array: UE 2010 20% + UE 2010 15%
0.00187
0.02962
0.00210
0.03431
0.01821
table 1: Root mean square
errors for the calibration and prediction of the data measured by the array
setup using 6 polymer sensors (1st row) and using all combinations
for 2 sensors out of 6 sensors (3rd row to 17th row) .
The root mean square errors for the miniaturized 4l setup, which uses 2 sensors, are listed
in the 2nd row.