Singular Value Decomposition is used as a Chemo
metric Tool for Kinetic Investigations
Mushini Venkata
Subba Rao1*, Ananta
Ramam V.2, Muralidhara
Rao V.2 and Sambasiva
Rao R.2
1Dept. of Chemistry,
G M R Institute of Technology, Rajam 532 127, Andhra
Pradesh, India.
2School of
Chemistry, Andhra University, Visakhapatnam 530 003, Andhra Pradesh, India
*Corresponding Author Email: subbarao.mv@gmrit.org, srmushini@rediffmail.com
ABSTRACT:
Singular Value Decomposition (SVD) is a
matrix based chemo metric tool, working under windows environment, and is used
to test several data sets namely “simulated”,” literature reported” and
“experimental”. Singular Value Decomposition employs the use of eigen value analysis for
identifying the number of species present in a reaction.
KEY WORDS: Chemometrics, SVD, Kinetics,
species.
INTRODUCTION:
Chemometrics1-4 comprises
Chemistry, advanced Mathematics, Statistics and Information theory. It is an interdisciplinary area emerged in
late 1970's. With the advent of chemometrics, multi-variate and
multi response data acquisition from statistically designed experiments, an
expert system inferences5 results in reliable chemical information
even in noisy environment.
Kinetometrics, a subfield of chemo
metrics deals with the knowledge of rates of chemical reaction and mechanistic
details. The scope of chemo metrics in
kinetic investigations is already reported6-8 by a few workers. A
few popular subfields are envirometrics9,10,
pharmacometrics, synthometrics,
qualimetrics and speciometrics11.
Singular Value
Decomposition (SVD) of a matrix or a second order tensor is a linear
mathematical decomposition into the influence of row designees (U), the
importance of each influence (diagonal element (S)) and the corresponding
influence of column designees (V). U and
V are orthogonal matrices. The power of
SVD is best used by selecting the statistically significant positive singular
values.
Truncated SVD obtained
by deleting all zeros and insignificant singular values together with their
corresponding vectors is useful to reproduce data matrix. SVD finds extensive
application in multivariate quantitative analysis using UV-Visible, NIR (Near infrared)
and excitation - emission spectra.
This technique can
also be applied in kinetic studies for identifying the number of reactant and
product species and to determine the number of independent reaction paths
contributing to the rate law.
Data reduction
technique:
A linear or non-linear
model can represent the variation of response or its function with the
magnitude of the influencing factors.
For instance, in a linear model y = a0 + a1x, all
the data points are reproducible by the parameters a0 and a1.
This is a data reduction technique as the number of parameters is far less than
the number of data points. Variation of absorbance(Y) with concentration
(Beer’s law) or logk(Y) with substituent (X) (Hammet equation) is a well-known linear model. The slopes and intercepts of these models
bear chemical significance. In the case
of non-linear models and polynomial models, the number of parameters increases
with order of the polynomial.
Dimension reduction technique:
The other situation is
the response or its function (Y) dependence on a number of influencing factors
like X1, X2, and X3. The following are to be considered for
analyzing and modeling.
·
Are the variables are to be correlated
·
Which variables are to be selected with the constraint that
each is independent of the other?
For example,
estimation of number of species from absorbance data over a range of
wavelengths is a dimension reduction technique.
Singular Value Decomposition (SVD), Principle Component Analysis (PCA)
and Factor Analysis (FA) are used in dimension reduction of chemical data.
Eigen values and Eigen
vectors:
Eigen values, also
called hidden roots, find extensive applications in quantum chemistry,
multivariate quantitative analysis and in solution processes. Many physico-chemical
phenomena in multi-dimensional space can be expressed as eigen problems. Similarly, the number of independent
reaction paths contributing to the rate law is equal to the number of eigen values of kinetic data
matrix. The use of eigen
value analysis for identifying the number of species is presented with data
sets which are simulated, literature reported and experimental.
In this paper, SVD
technique is used for identifying the number of species involved in a kinetic
investigation. For identifying the number of species a few simulated data sets and reported data
sets with Methyl red, chloranilic acid and Hf-chloranilic acid have been chosen. The experimental data obtained “on the
spectrophotometric studies. The spectra of hexaaquochromium(III)
absorbance values at different pH
conditions are taken and are analyzed by SVD technique. And also the other
experimental data obtained from the
substitution reaction of hexaaquochromium(III) with EDTA has
been analyzed by SVD technique.
Hardware and software:
An IBM Pentium II
Computer is used for analyzing data.
MATLAB (Version 4.2c.1 for Windows environment) from Math Works Inc. is
employed to develop programs and graphic outputs. MVATOB is developed from the subset of method
based in matrix notation. MVATOB
consists of SVD among others like MLR, PCA2, PLSC1 m-files. This package was thoroughly tested with
several data sets (simulated, literature reported and experimental data).
EXPERIMENTAL AND RESULT ANALYSIS:
Simulated data sets:
Example 1:
The angle between column vectors of the
data set
Example 2:
The vectors of the
data set
Literature reported
data sets:
Example 1: Methyl red
The spectra of Methyl
red12 (8´8 matrix) in the pH
range (2.20-6.60) have one maximum, but the isobestic
point and eigen vector
analysis indicate the presence of two species.
The absorbance matrix in Table 1A is highly correlated with the matrix
in Table 1B. Representing the residuals in absorbance after considering eigen
values upto 1, 2 and 3, it is
evident that the residuals are
high when eigen value is one, where as the residuals
are within the range ± 0.03 with two eigen values. This
indicates the existence of two species.
Model with three eigen
values appears to be over ambitious (over fitting). Similar conclusions are drawn with a data
matrix of 4´4 size, but with
inferior quality. When drawn in scree plot, the result unequivocally establishes the
presence of two species within the experimental pH range (2.20-6.60). The first
two Eigen values explain 74.40 % and 23.82 % (Table 1C).
Table 1A. Spectra of Methyl red at different pH values
|
pH |
Absorbance at the wavelengths (nm) |
|||||||
|
400 |
425 |
450 |
475 |
500 |
525 |
550 |
575 |
|
|
2.20 |
0.017 |
0.045 |
0.062 |
0.110 |
0.197 |
0.278 |
0.332 |
0.377 |
|
3.00 |
0.058 |
0.080 |
0.100 |
0.152 |
0.238 |
0.320 |
0.372 |
0.417 |
|
3.40 |
0.167 |
0.180 |
0.187 |
0.222 |
0.282 |
0.330 |
0.368 |
0.400 |
|
3.80 |
0.420 |
0.402 |
0.395 |
0.365 |
0.342 |
0.310 |
0.300 |
0.292 |
|
4.60 |
0.770 |
0.735 |
0.690 |
0.565 |
0.437 |
0.278 |
0.192 |
0.131 |
|
5.40 |
1.015 |
0.990 |
0.922 |
0.742 |
0.528 |
0.282 |
0.147 |
0.051 |
|
6.20 |
0.935 |
0.940 |
0.875 |
0.702 |
0.488 |
0.255 |
0.118 |
0.032 |
|
6.60 |
0.443 |
0.480 |
0.462 |
0.342 |
0.235 |
0.108 |
0.048 |
0.015 |
Table 1B. Correlation matrix of
Methyl red
|
|
X1 |
X2 |
X3 |
X4 |
X5 |
X6 |
X7 |
X8 |
|
X1 |
1.00 |
|
|
|
|
|
|
|
|
X2 |
1.00 |
1.00 |
|
|
|
|
|
|
|
X3 |
1.00 |
1.00 |
1.00 |
|
|
|
|
|
|
X4 |
1.00 |
0.99 |
0.99 |
1.00 |
|
|
|
|
|
X5 |
0.94 |
0.93 |
0.93 |
0.96 |
1.00 |
|
|
|
|
X6 |
-0.20 |
-0.24 |
-0.24 |
-0.14 |
0.13 |
1.00 |
|
|
|
X7 |
-0.75 |
-0.77 |
-0.77 |
-0.71 |
-0.49 |
0.80 |
1.00 |
|
|
X8 |
-0.86 |
-0.88 |
-0.88 |
-0.82 |
-0.64 |
0.68 |
0.98 |
1.00 |
Table 1C.
Percentage explainability of Methyl red
|
Eigen values |
Percentage explainability (PE) |
Cumulative percentage explainability
(CPE) |
Landa |
|
1 |
74.4075 |
74.4075 |
11.5782 |
|
2 |
23.8232 |
98.0307 |
1.1671 |
|
3 |
1.2516 |
99.2823 |
0.003276 |
|
4 |
0.39288 |
99.6751 |
0.00032283 |
Example 2: Acido basic equilibria of chloranilic acid
The spectra of
chloranilic13 acid (21 ´ 12 matrix) at different acid concentrations are taken for analysis.The absorbance values of chloranilic
acid13 for solutions with 12 concentrations of the acid are recorded
as a function of wavelength (Table 2A).
Contour plots are drawn and 2D representation of 3D surface in variable axes as iso-response
values. Each iso-contour
represents the lines of equal
responses. It gives quantitative
information of the variation of the response with the simultaneous variation of
the two variables.
The correlation
between column vectors is 1.0 and angle is < 3°. All the variance (99.96 %) in
the absorbance matrix is explained by the first eigen vector (Table 2B). The chemical validity of one species for chloranilic acid in 3M perchloric
acid comes from the fact that no ionization takes place at this acid
concentration and clearly demonstrates the presence of one species for chloranilic acid.
Table
2A . Spectra of chloranilic
acid of different concentrations
|
|
Absorbance values of [H2Ch]
X 104, mol dm-3 |
|||||||||||
|
Wave length (nm) |
0.08 |
0.16 |
0.24 |
0.32 |
0.40 |
0.48 |
0.56 |
0.64 |
0.72 |
0.80 |
0.88 |
0.96 |
|
360 |
0.007 |
0.007 |
0.008 |
0.009 |
0.012 |
0.012 |
0.012 |
0.012 |
0.031 |
0.023 |
0.031 |
0.027 |
|
355 |
0.007 |
0.007 |
0.008 |
0.010 |
0.012 |
0.012 |
0.012 |
0.014 |
0.032 |
0.024 |
0.037 |
0.029 |
|
350 |
0.007 |
0.007 |
0.009 |
0.011 |
0.012 |
0.012 |
0.012 |
0.016 |
0.033 |
0.025 |
0.038 |
0.031 |
|
345 |
0.007 |
0.007 |
0.010 |
0.012 |
0.013 |
0.013 |
0.013 |
0.018 |
0.037 |
0.027 |
0.038 |
0.032 |
|
340 |
0.007 |
0.007 |
0.011 |
0.012 |
0.014 |
0.017 |
0.017 |
0.021 |
0.042 |
0.032 |
0.046 |
0.037 |
|
335 |
0.007 |
0.008 |
0.013 |
0.017 |
0.018 |
0.017 |
0.020 |
0.023 |
0.048 |
0.037 |
0.054 |
0.045 |
|
330 |
0.008 |
0.010 |
0.018 |
0.022 |
0.026 |
0.028 |
0.030 |
0.037 |
0.064 |
0.053 |
0.073 |
0.061 |
|
325 |
0.013 |
0.016 |
0.032 |
0.038 |
0.049 |
0.056 |
0.062 |
0.075 |
0.107 |
0.101 |
0.123 |
0.122 |
|
320 |
0.027 |
0.048 |
0.073 |
0.096 |
0.117 |
0.136 |
0.158 |
0.182 |
0.230 |
0.237 |
0.275 |
0284 |
|
315 |
0.062 |
0.114 |
0.173 |
0.232 |
0.288 |
0.342 |
0.398 |
0.452 |
0.544 |
0.574 |
0.650 |
0.688 |
|
310 |
0.114 |
0.231 |
0.343 |
0.456 |
0.571 |
0.678 |
0.792 |
0.895 |
1.047 |
1.133 |
1.272 |
1.348 |
|
305 |
0.158 |
0.317 |
0.473 |
0.627 |
0.782 |
0.935 |
1.098 |
1.237 |
1.430 |
1.536 |
1.734 |
1.808 |
|
300 |
0.163 |
0.324 |
0.487 |
0.642 |
0.803 |
0.960 |
1.118 |
1.273 |
1.464 |
1.573 |
1.757 |
1.893 |
|
295 |
0.146 |
0.288 |
0.438 |
0.572 |
0.725 |
0.860 |
1.005 |
1.132 |
1.332 |
1.414 |
1.598 |
1.723 |
|
290 |
0.122 |
0.239 |
0.361 |
0.482 |
0.603 |
0.720 |
0.835 |
0.962 |
1.127 |
1.218 |
1.351 |
1.436 |
|
285 |
0.091 |
0.177 |
0.270 |
0.358 |
0.448 |
0.528 |
0.614 |
0.700 |
0.845 |
0.900 |
1.018 |
1.072 |
|
280 |
0.062 |
0.118 |
0.183 |
0.222 |
0.308 |
0.359 |
0.422 |
0.478 |
0.593 |
0.618 |
0.712 |
0.740 |
|
275 |
0.039 |
0.078 |
0.116 |
0.158 |
0.198 |
0.222 |
0.264 |
0.306 |
0.404 |
0.405 |
0.474 |
0.465 |
|
270 |
0.026 |
0.043 |
0.071 |
0.097 |
0.123 |
0.137 |
0.158 |
0.185 |
0.269 |
0.254 |
0.315 |
0.304 |
|
265 |
0.014 |
0.024 |
0.043 |
0.058 |
0.075 |
0.077 |
0.088 |
0.107 |
0.106 |
0.156 |
0.208 |
0.183 |
|
260 |
0.011 |
0.012 |
0.026 |
0.034 |
0.040 |
0.044 |
0.048 |
0.063 |
0.138 |
0.098 |
0.148 |
0.117 |
The number of
significant eigen values are
arrived at based on statistical tests like IE, XE, FIND etc. The further
information related to statistical tests are given below.
RSD
= SUM (LANDA) / RX / (CX-NPE)
IE
=
XE =
RE =
FIND =
F1, c-p =
(CX-NPE)*LANDA (NPE) /
SUM (LANDA (NPE + 1:
CX))
RX, CX: Rows and
columns; LANDA: eigen values
NPE: No. of primary eigen values
IE: Imbedded error
FIND: Factor indicator
function
RE: Residual error
XE: Extracted error
Example 3: Hafnium-chloranilic
acid
Chloranilic acid HL, forms ML and
ML2 type of complexes with metal ions like Hf
and Zr. Thus,
one expects three absorbing species viz., ML, ML2 and free HL in 3M perchloric acid.
Table 3A represents
the spectra of Hf-chloranilic acid13 at
different wavelengths. This is a data
matrix of the size 20´12 and use this to
find the eigen values. The three eigen values explain to an extent of 99.96% (Table
3B) which establishes clearly the presence of three species. The absorption spectra of chloranilic
acid and ML overlap largely indicating two maxima in the 3D surface and contour
diagram .The scree plot and modified scree plot as well as the different tests implemented by
Malinowski14 parameters and as clearly demonstrate the presence of
three species for Hf - Chloranilic
acid.
Table 2B.
Percentage explainability of Chloranilic acid
|
Eigen values |
Percentage explainability (PE) |
Cumulative
percentage explainability (CPE) |
Landa |
|
1 |
99.96 |
99.96 |
75.8 |
|
2 |
0.02089 |
99.99 |
0.01584 |
|
3 |
0.01111 |
100.00 |
0.008424 |
EXPERIMENTAL DATA SETS:
Example 1: Hydrolysis
of hexaaquochromium(III)
The spectra (370-700
nm) has been recorded of hexaaquo- chromium (III)
(5.0´10-2 mol dm-3) in
the pH range (3.00-5.00) with Milton Roy Spectronic
1201 spectrophotometer. The data matrix (70´5) of the spectra is represented in Table 4A. The absorption spectra are
plotted in 2D (Figure 1a). The spectra show two maxima, one around 420 nm and
the other at around 578 nm. With increase
in pH, there is an increase in absorbance value as well as a slight shift in
the wavelength of maximum absorption.
Eigen vector analysis indicates the presence of two species [(Cr(H2O)63+ and Cr(H2O)5(OH)2+]. The first two eigen values explain 93.99% and 3.38% variance in
data matrix as seen in Table 4B.
Table 3A.
Spectra of Hf-Chloranilic acid
complex
|
|
Absorbance values at different
mole ratios of chloranic acid to Hafnium [Chloranic acid]
= 0.08 to 0.96 X 10-4 M
[Hf]
= 0.92 to 0.04 X 10-4 M |
|||||||||||
|
Wave length (nm) |
0.087 |
0.190 |
0.316 |
0.471 |
0.667 |
0.923 |
1.28 |
1.79 |
2.59 |
4.00 |
7.33 |
24.0 |
|
360 |
0.020 |
0.024 |
0.034 |
0.038 |
0.042 |
0.042 |
0.043 |
0.038 |
0.037 |
0.032 |
0.022 |
0.018 |
|
355 |
0.028 |
0.041 |
0.051 |
0.062 |
0.067 |
0.068 |
0.069 |
0.066 |
0.062 |
0.053 |
0.037 |
0.027 |
|
350 |
0.038 |
0.062 |
0.081 |
0.092 |
0.103 |
0.109 |
0.107 |
0.098 |
0.093 |
0.076 |
0.055 |
0.032 |
|
345 |
0.053 |
0.088 |
0.114 |
0.136 |
0.145 |
0.154 |
0.150 |
0.143 |
0.128 |
0.105 |
0.075 |
0.040 |
|
340 |
0.066 |
0.116 |
0.152 |
0.177 |
0.196 |
0.203 |
0.201 |
0.188 |
0.169 |
0.138 |
0.100 |
0.053 |
|
335 |
0.080 |
0.138 |
0.182 |
0.214 |
0.225 |
0.248 |
0.242 |
0.228 |
0.203 |
0.167 |
0.118 |
0.066 |
|
330 |
0.087 |
0.152 |
0.200 |
0.241 |
0.266 |
0.279 |
0.275 |
0.258 |
0.234 |
0.194 |
0.143 |
0.087 |
|
320 |
0.090 |
0.162 |
0.207 |
0.272 |
0.317 |
0.338 |
0.353 |
0.362 |
0.357 |
0.345 |
0.317 |
0.286 |
|
315 |
0.096 |
0.178 |
0.252 |
0.321 |
0.388 |
0.443 |
0.494 |
0.541 |
0.582 |
0.613 |
0.625 |
0.670 |
|
310 |
0.108 |
0.211 |
0.313 |
0.417 |
0.516 |
0.620 |
0.737 |
0.845 |
0.960 |
1.056 |
1.166 |
1.287 |
|
305 |
0.118 |
0.232 |
0.353 |
0.476 |
0.616 |
0.765 |
0.915 |
1.067 |
1.242 |
1.409 |
1.580 |
1.726 |
|
300 |
0.114 |
0.223 |
0.338 |
0.464 |
0.607 |
0.747 |
0.900 |
1.064 |
1.268 |
1.452 |
1.695 |
1.775 |
|
295 |
0.109 |
0.202 |
0.302 |
0.382 |
0.534 |
0.663 |
0.803 |
0.944 |
1.161 |
1.317 |
1.478 |
1.630 |
|
290 |
0.112 |
0.186 |
0.268 |
0.359 |
0.459 |
0.573 |
0.686 |
0.805 |
1.026 |
1.163 |
1.293 |
1.425 |
|
285 |
0.113 |
0.169 |
0.231 |
0.296 |
0.373 |
0.454 |
0.538 |
0.623 |
0.862 |
0.967 |
1.038 |
1.147 |
|
280 |
0.118 |
0.158 |
0.202 |
0.249 |
0.300 |
0.352 |
0.406 |
0.466 |
0.732 |
0.792 |
0.820 |
0.910 |
|
275 |
0.127 |
0.156 |
0.184 |
0.213 |
0.249 |
0.282 |
0.314 |
0.350 |
0.633 |
0.675 |
0.673 |
0.720 |
|
270 |
0.137 |
0.152 |
0.168 |
0.192 |
0.206 |
0.227 |
0.248 |
0.267 |
0.575 |
0.594 |
0.564 |
0.595 |
|
265 |
0.137 |
0.150 |
0.162 |
0.173 |
0.191 |
0.197 |
0.206 |
0.213 |
0.533 |
0.537 |
0.492 |
0.505 |
|
260 |
0.134 |
0.144 |
0.154 |
0.163 |
0.176 |
0.177 |
0.182 |
0.183 |
0.492 |
0.488 |
0.441 |
0.445 |
Table 3B . Percentage explainability
of Hf- Chloranilic acid
|
Eigen values |
Percentage explainability (PE) |
Cumulative
percentage explainability (CPE) |
Landa |
|
1 |
90.4019 |
90.4019 |
206.1163 |
|
2 |
6.2658 |
96.6677 |
14.2860 |
|
3 |
3.2905 |
99.9582 |
7.5024 |
|
4 |
0.017708 |
99.9759 |
0.04037 |
|
5 |
0.010497 |
99.9864 |
0.02393 |
|
6 |
0.0080483 |
99.9944 |
0.01835 |
Table 4A.
Hydrolysis of Hexaaquochromium(III) at different pH values
|
Wave Length (nm) |
Absorbance values at different
pH values [Cr(H2O)63+]
= 5.0 ´ 10-2 mol dm-3 , t / oC = 30.0 ±
0.1 |
||||
|
|
3.00 |
3.50 |
4.00 |
4.50 |
5.00 |
|
370 |
0.300 |
0.321 |
0.331 |
0.330 |
0.303 |
|
380 |
0.445 |
0.471 |
0.487 |
0.494 |
0.476 |
|
390 |
0.606 |
0.637 |
0.664 |
0.687 |
0.694 |
|
400 |
0.764 |
0.812 |
0.858 |
0.894 |
0.920 |
|
402 |
0.783 |
0.838 |
0.885 |
0.922 |
0.955 |
|
404 |
0.797 |
0.857 |
0.911 |
0.952 |
0.985 |
|
406 |
0.804 |
0.870 |
0.930 |
0.970 |
1.007 |
|
408 |
0.810 |
0.887 |
0.949 |
0.994 |
1.031 |
|
410 |
0.813 |
0.894 |
0.966 |
1.011 |
1.050 |
|
412 |
0.814 |
0.904 |
0.986 |
1.027 |
1.066 |
|
414 |
0.813 |
0.912 |
0.994 |
1.040 |
1.079 |
|
416 |
0.811 |
0.917 |
1.007 |
1.052 |
1.091 |
|
418 |
0.805 |
0.921 |
1.018 |
1.063 |
1.101 |
|
420 |
0.797 |
0.923 |
1.023 |
1.070 |
1.108 |
|
422 |
0.790 |
0.926 |
1.034 |
1.079 |
1.115 |
|
424 |
0.770 |
0.913 |
1.027 |
1.072 |
1.106 |
|
426 |
0.752 |
0.906 |
1.024 |
1.068 |
1.101 |
|
428 |
0.745 |
0.904 |
1.030 |
1.072 |
1.103 |
|
430 |
0.754 |
0.904 |
1.047 |
1.088 |
1.117 |
|
432 |
0.734 |
0.904 |
1.039 |
1.078 |
1.107 |
|
434 |
0.713 |
0.889 |
1.025 |
1.063 |
1.091 |
|
436 |
0.691 |
0.871 |
1.010 |
1.046 |
1.073 |
|
438 |
0.666 |
0.851 |
0.990 |
1.025 |
1.050 |
|
440 |
0.643 |
0.829 |
0.970 |
1.002 |
1.026 |
|
450 |
0.532 |
0.805 |
0.850 |
0.872 |
0.880 |
|
460 |
0.426 |
0.591 |
0.712 |
0.725 |
0.722 |
|
470 |
0.345 |
0.487 |
0.588 |
0.593 |
0.578 |
|
480 |
0.292 |
0.399 |
0.473 |
0.471 |
0.448 |
|
490 |
0.274 |
0.347 |
0.397 |
0.394 |
0.368 |
|
500 510 |
0.279 0.311 |
0.328 0.343 |
0.361 0.367 |
0.362 0.374 |
0.341 0.362 |
|
520 |
0.362 |
0.384 |
0.405 |
0.422 |
0.422 |
|
530 |
0.430 |
0.448 |
0.469 |
0.497 |
0.497 |
|
532 |
0.445 |
0.462 |
0.483 |
0.513 |
0.529 |
|
534 |
0.459 |
0.475 |
0.497 |
0.528 |
0.548 |
|
536 |
0.473 |
0.489 |
0.512 |
0.545 |
0.568 |
|
538 |
0.487 |
0.504 |
0.528 |
0.564 |
0.589 |
|
540 |
0.503 |
0.520 |
0.544 |
0.583 |
0.611 |
|
542 |
0.518 |
0.534 |
0.560 |
0.600 |
0.632 |
|
544 |
0.531 |
0.548 |
0.574 |
0.616 |
0.651 |
|
546 |
0.545 |
0.562 |
0.590 |
0.636 |
0.671 |
|
548 |
0.559 |
0.577 |
0.605 |
0.651 |
0.692 |
|
550 |
0.572 |
0.590 |
0.619 |
0.667 |
0.712 |
|
552 |
0.582 |
0.601 |
0.631 |
0.682 |
0.729 |
|
554 |
0.596 |
0.615 |
0.647 |
0.699 |
0.750 |
|
556 |
0.607 |
0.626 |
0.660 |
0.714 |
0.766 |
|
558 |
0.616 |
0.637 |
0.671 |
0.727 |
0.781 |
|
560 |
0.627 |
0.648 |
0.683 |
0.741 |
0.799 |
|
562 |
0.638 |
0.661 |
0.696 |
0.756 |
0.817 |
|
564 |
0.646 |
0.669 |
0.707 |
0.768 |
0.831 |
|
566 |
0.652 |
0.677 |
0.714 |
0.777 |
0.844 |
|
568 |
0.657 |
0.682 |
0.721 |
0.785 |
0.853 |
|
570 |
0.661 |
0.687 |
0.728 |
0.793 |
0.863 |
|
572 |
0.665 |
0.692 |
0.733 |
0.800 |
0.872 |
|
574 |
0.667 |
0.695 |
0.738 |
0.805 |
0.881 |
|
576 |
0.668 |
0.697 |
0.741 |
0.809 |
0.886 |
|
578 |
0.669 |
0.699 |
0.743 |
0.812 |
0.890 |
|
580 |
0.667 |
0.699 |
0.744 |
0.815 |
0.893 |
|
590 |
0.647 |
0.685 |
0.736 |
0.807 |
0.889 |
|
600 |
0.605 |
0.649 |
0.704 |
0.772 |
0.857 |
|
610 |
0.542 |
0.592 |
0.651 |
0.717 |
0.798 |
|
620 |
0.471 |
0.527 |
0.585 |
0.645 |
0.716 |
|
630 |
0.395 |
0.451 |
0.510 |
0.557 |
0.615 |
|
640 |
0.332 |
0.390 |
0.447 |
0.485 |
0.531 |
|
650 |
0.268 |
0.327 |
0.382 |
0.413 |
0.453 |
|
660 |
0.217 |
0.273 |
0.321 |
0.345 |
0.373 |
|
670 |
0.192 |
0.240 |
0.278 |
0.294 |
0.310 |
|
680 |
0.155 |
0.201 |
0.238 |
0.252 |
0.266 |
|
690 |
0.122 |
0.165 |
0.200 |
0.211 |
0.224 |
|
700 |
0.099 |
0.136 |
0.163 |
0.169 |
0.176 |
Table 4B. Singular values and percentage explainability
|
Eigen values |
Singular value |
Percentage explainability |
Cumulative percentage explainability |
Landa |
|
1 |
13.3958 |
93.9968 |
93.9968 |
179.4484 |
|
2 |
0.48266 |
3.3868 |
97.3836 |
0.23296 |
|
3 |
0.24918 |
1.7484 |
99.1321 |
0.062089 |
|
4 |
0.072726 |
0.51031 |
99.6434 |
0.0052891 |
|
5 |
0.050966 |
0.35762 |
100.00 |
0.0025976 |
Table 4C.
Malonowski Parameters
|
Landa |
I.E |
RE |
XE |
FIND |
RMS |
ER |
|
179.4484 |
0.01471 |
0.032893 |
0.02942 |
0.016446 |
0.30294 |
770.2831 |
|
0.23296 |
0.011545 |
0.018254 |
0.01414 |
0.010539 |
0.017494 |
3.7521 |
|
0.062089 |
0.0058138 |
0.0075055 |
0.0047469 |
0.0053072 |
0.00087629 |
11.7391 |
|
0.0052891 |
0.0054485 |
0.0060916 |
0.0027243 |
0.0060916 |
0.00016235 |
2.0362 |
Table 5A. Kinetic spectra of Hexaaquochromium(III) with
EDTA
|
|
Absorbance values at different
Wavelengths(nm) |
||||||
|
[Cr(H2O)63+]
= 4.0 ´ 10-
3 mol dm-3 ; [EDTA] =
8.0 ´ 10-2 mol dm-3 m = 1.0 M,
pH = 4.00 , t / oC = 30.0 ± 0.1 |
|||||||
|
Time minutes |
520 |
530 |
540 |
545 |
550 |
560 |
570 |
|
0.30 |
0.040 |
0.047 |
0.054 |
0.057 |
0.060 |
0.066 |
0.068 |
|
2 |
0.051 |
0.059 |
0.066 |
0.070 |
0.074 |
0.079 |
0.083 |
|
4 |
0.068 |
0.079 |
0.089 |
0.094 |
0.098 |
0.103 |
0.105 |
|
6 |
0.097 |
0.113 |
0.124 |
0.130 |
0.133 |
0.136 |
0.137 |
|
8 |
0.132 |
0.150 |
0.164 |
0.169 |
0.172 |
0.174 |
0.171 |
|
10 |
0.170 |
0.192 |
0.206 |
0.210 |
0.214 |
0.212 |
0.207 |
|
12 |
0.208 |
0.231 |
0.248 |
0.252 |
0.253 |
0.249 |
0.239 |
|
14 |
0.244 |
0.270 |
0.285 |
0.289 |
0.291 |
0.284 |
0.270 |
|
16 |
0.274 |
0.305 |
0.322 |
0.326 |
0.326 |
0.317 |
0.300 |
|
18 |
0.307 |
0.338 |
0.356 |
0.357 |
0.358 |
0.348 |
0.326 |
|
20 |
0.334 |
0.367 |
0.384 |
0.387 |
0.385 |
0.373 |
0.350 |
|
22 |
0.360 |
0.394 |
0.410 |
0.413 |
0.412 |
0.397 |
0.371 |
|
24 |
0.382 |
0.417 |
0.435 |
0.437 |
0.435 |
0.418 |
0.391 |
|
26 |
0.403 |
0.440 |
0.457 |
0.458 |
0.457 |
0.439 |
0.408 |
|
28 |
0.421 |
0.459 |
0.476 |
0.478 |
0.476 |
0.454 |
0.425 |
|
30 |
0.437 |
0.477 |
0.494 |
0.494 |
0.492 |
0.472 |
0.440 |
|
32 |
0.452 |
0.492 |
0.511 |
0.509 |
0.508 |
0.484 |
0.452 |
|
34 |
0.466 |
0.506 |
0.526 |
0.525 |
0.521 |
0.499 |
0.465 |
|
36 |
0.479 |
0.520 |
0.538 |
0.539 |
0.534 |
0.510 |
0.474 |
|
38 |
0.490 |
0.531 |
0.548 |
0.552 |
0.549 |
0.522 |
0.483 |
|
40 |
0.500 |
0.543 |
0.561 |
0.561 |
0.557 |
0.532 |
0.495 |
|
45 |
0.521 |
0.567 |
0.585 |
0.587 |
0.582 |
0.555 |
0.515 |
|
50 |
0.541 |
0.587 |
0.605 |
0.606 |
0.601 |
0.572 |
0.530 |
|
55 |
0.556 |
0.603 |
0.622 |
0.623 |
0.614 |
0.588 |
0.543 |
|
60 |
0.569 |
0.617 |
0.635 |
0.636 |
0.631 |
0.602 |
0.557 |
|
65 |
0.580 |
0.629 |
0.647 |
0.649 |
0.642 |
0.612 |
0.566 |
|
70 |
0.591 |
0.639 |
0.659 |
0.658 |
0.652 |
0.621 |
0.576 |
|
75 |
0.599 |
0.649 |
0.669 |
0.668 |
0.662 |
0.630 |
0.582 |
|
80 |
0.606 |
0.658 |
0.677 |
0.676 |
0.669 |
0.637 |
0.590 |
|
85 |
0.613 |
0.665 |
0.683 |
0.683 |
0.674 |
0.643 |
0.595 |
|
90 |
0.620 |
0.672 |
0.690 |
0.690 |
0.679 |
0.649 |
0.600 |
Table 5B. Singular values and percentage explainability of Hexaaquochromim
(III) with EDTA
|
Eigen values |
Singular value |
Percentage explainability |
Cumulative percentage explainability |
Landa |
|
1 |
6.838 |
98.2394 |
98.2394 |
46.7586 |
|
2 |
0.098612 |
1.4167 |
99.6562 |
0.0097243 |
|
3 |
0.0073557 |
0.10598 |
99.7618 |
5.4106e-005 |
|
4 |
0.0052137 |
0.074904 |
99.8367 |
2.7183e-005 |
|
5 |
0.0048736 |
0.070017 |
99.9068 |
2.3752e-005 |
|
6 |
0.003607 |
0.051821 |
99.9586 |
1.3011e-005 |
|
7 |
0.0028833 |
0.041423 |
100.00 |
8.3133e-006 |
Figure 1a.
Absorbance spectra of Chromium (III) at different pH Values
Residuals in the
absorbance values considering eigen
values up to 1,2,3,4 and 5 are calculated.
The results clearly demonstrate the residuals are less than ± 0.01 absorbance units when first two eigen values are considered. Further, the presence of
two species is confirmed by scree plot, modified scree plot and from the plots of the different errors vs eigen
values [Figure 1b, Table 4C].
Example 2: Kinetics of Hexaaquochromium(III) with
EDTA
12.5 ml of disodium
salt of EDTA (0.16M) solution is taken in 50 ml beaker and the ionic strength (m=1.0) is maintained with sodium perchlorate. This
solution is adjusted to the pH 4.00 using dilute solution of sodium hydroxide
and quantitatively transferred into 25ml volumetric flask. A 2.5 ml portion of hexaaquochromium(III)
solution is added to it and made up to the mark with distilled water. Immediately the solution is transferred into
the optical cell and the absorbance values are taken at multiple wavelengths
(520 nm-570 nm) at 30.0 °C as a function of
time (Table 5A). The data matrix is of
the size of 31´7. The absorbance time
profiles at different wavelengths and 3D surface plot of absorbance vs time and wavelength are seen in figure 2a respectively.
Figure 2b shows the isoabsorbance surface of time vs wavelength. The eigen vector analysis indicates the presence of two species
[Cr(H2O)63+ and Cr(EDTA)(H2O)-1
].Basing on the singular values and percentage explainability
(Table 5B) the first two eigen values explain 98.23%
and 1.41%. The residuals in absorbance
after considering eigen
values 1, 2 and 3 are pictorially represented in figure 2c. The residuals in the range of ± 3´10-3
(absorbance) units when two eigen
values are used indicates the presence of two species.
Figure 1b. The number of eigen values vs
errors (Based on different statistical tests)
Figure 2a. 3D surface plot Absorbance vs
time vs wavelength
X is attribute
Figure 2b.
Isoresponse surface of wavelength vs
time; X is attribute
CONCLUSIONS:
SVD technique is used
for identifying the number of species involved in a kinetic investigation. We
examined the simulated data sets, literature reported
data sets and experimental data sets by using this chemo metric tool. In this
process, the identified number of species in a particular reaction is well in
agreement with experimental. Therefore, we are suggesting this method for
identifying the number of species in a chemical reaction by using the S V D
technique.
Figure 2c.Eigen values.
REFERENCES:
1.
Kowalski B R 1977 Chemo metrics: Theory and application,
ACS Symposium series, American Chemical
Society, U S A.
2.
(a) Lavine B K 2002 Anal.Chem. 74 2763
(b) Lavine B K, Davidson C E and Westover D J 2004 J.Chem.Inf.Comp.Science. 44 1056
(c) Lavine B K and Workmann J R 2004 Anal.Chem. 76 3365
(d) Lavine B K 2000 Anal.Chem.72 91R
(e) Lavine B K 1998 Anal.Chem.
70 209R
(f) Brown
S D, Sum S T and Despagne F 1996 Anal.Chem.68
21R
(g) Brown
S D, Blank T B, Tum S T and Weyerl L G
1994 Anal.Chem.
66 315R
(h) Brown
S D, Bear R S and
Blank T B 1992 Anal.Chem. 64
22R
(i) Brown S D 1990 Anal.Chem.
62 84R
(j) Brown
S D, Baker T Q, Larivee
R J, Monfre S
L and Wilk H R 1998 Anal.Chem. 60 252R.
(k) Ramos
L S, Beebe K R, Carey W P, Sanchez E M , Erickson B C, Wilson B E,
Wangen L E and Kowalski B R 1986 Anal.Chem. 58 294R
(l) Delaney
M F 1984 Anal.Chem.
56 261R
(m) Frnak I E and Kowalski B R 1982 Anal.Chem. 54 232R
(n) Kowalski B R 1980 Anal.Chem.
52 112R
(o) Geladi P
and Esbensen K The start and early
history of chemometrics: Selected interviews. Part 1 2005 J. Chemometrics 4
337
(p) Esbensen K and Geladi P The start and early history of chemometrics:
Selected interviews. Part 2 2005 J. Chemometrics 4 389
(q) Brown S D, Tauler
R and Walczak B (eds) 2009 Comprehensive
Chemometrics: chemical and biochemical data analysis
(4 volume set) Elsevier
(r) Otto
M 2007 Chemometrics:statistics
and computer application in analytica Chemistry 2nd Edition, Wiley-VCH
3. Windows on Chemometrics(monthly), The Royal society of Chemistry, Milton Road,
Cambridge, CB4 4WF ,UK.
4. Nageswara Rao G, Sambasiva Rao K, Sambasiva Rao R, Abdel Rehman R L H 2000 J.Indian Council Of
chemists. 17 48
5. Priyabrunda G, Nageswara Rao G, Sambasiva Rao R 1997 J.T.R.Chem. 4 29
6. Nageswara Rao
G, Ananta
Ramam V, Satyanarayana Rao S V V and Sambasiva Rao R 1998 J.Indian Chem.Soc. 75 236
7. Ananta Ramam V, Nageswara Rao G, Ramasastry S V and Sambasiva Rao R 1997 Indian J.Chemistry. 36A 964
8. Nageswara Rao
G, Ananta Ramam V and Sambasiva Rao R 1997 Bull.Soc.Kinet.Ind. 19 1
9. Brainbanti A, Nageswara Rao G , Sreekanth Babu J, Sudarsan D and Sambasiva Rao R 2000 Annali di Chimica. 90 1
10. Panakala Rao V
V, Ananta Ramam V , Nageswara Rao G and Sambasiva Rao R 2000 Proceedings
of national seminar on
environmental Geology and waste management, Department of Geology,AndhraUniversity,Visakhapatnam p 125
11. Babu A R, Muralikrishna
D and Sambasiva Rao R 1993 Talanta. 40 1873
12. Wallace R M 1960 J.Phy.Chem. 64 899
13. Varga L P and Veatch F C 19647 Anal.Chem. 39 1101
14. Malinowski M R
1977 Anal.Chem. 49
612.
Received on 16.02.2013 Accepted
on 26.08.2013
Modified on 20.09.2013 ©A&V
Publications all right reserved
Research J. Science and Tech 5(4): Oct.- Dec.., 2013 page 412-420