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APPENDICES

413

 

 

Compute the Component and Calculate Residuals

7. Subtract the effect of the new PC from the datamatrix to obtain a residual

data matrix:

resid X = X t.p

Further PCs

8.If it is desired to compute further PCs, substitute the residual data matrix for X and go to step 2.

A.2.2 PLS1

There are several implementations; the one below is noniterative.

Initialisation

1.Take a matrix Z and, if required, preprocess (e.g. mean centre or standardise) to give the matrix X which is used for PLS.

2.Take the concentration vector k and preprocess it to give the vector c which is used for PLS. Note that if the data matrix Z is centred down the columns, the

concentration vector must also be centred. Generally, centring is the only form of preprocessing useful for PLS1. Start with an estimate of cˆ that is a vector of 0s (equal to the mean concentration if the vector is already centred).

New PLS Component

3. Calculate the vector

h = X .c

4. Calculate the scores, which are simply given by

X.h t =

h2

5. Calculate the x loadings by

t .X p =

t2

6. Calculate the c loading (a scalar) by

c .t q =

t2

Compute the Component and Calculate Residuals

7. Subtract the effect of the new PLS component from the data matrix to get a residual

data matrix:

resid X = X t.p

414 CHEMOMETRICS

8. Determine the new concentration estimate by

new cˆ = initial cˆ + t.q

and sum the contribution of all components calculated to give an estimated cˆ. Note that the initial concentration estimate is 0 (or the mean) before the first component has been computed. Calculate

resid c = true c new cˆ

where true c is, like all values of c, after the data have been preprocessed (such as centring).

Further PLS Components

9.If further components are required, replace both X and c by the residuals and return to step 3.

Note that in the implementation used in this text the PLS loadings are neither normalised nor orthogonal. There are several different PLS1 algorithms, so it is useful to check exactly what method a particular package uses, although the resultant concentration estimates should be identical for each method (unless there is a problem with convergence in iterative approaches).

A.2.3 PLS2

This is a straightforward, iterative, extension of PLS1. Only small variations are required. Instead of c being a vector it is now a matrix C and instead of q being a scalar it is now a vector q.

Initialisation

1.Take a matrix Z and, if required, preprocess (e.g. mean centre or standardise) to give the matrix X which is used for PLS.

2.Take the concentration matrix K and preprocess it to give the vector c which is used for PLS. Note that if the data matrix is centred down the columns, the concentration vector must also be centred. Generally, centring is the only form of

ˆ

preprocessing useful for PLS2. Start with an estimate of C that is a vector of 0s (equal to the mean concentration if the vector is already centred).

New PLS Component

3.An extra step is required to identify a vector u which can be a guess (as in PCA), but can be chosen as one of the columns in the initial preprocessed concentration matrix, C.

4.Calculate the vector

h = X .u

APPENDICES

415

 

 

5.

Calculate the guessed scores by

 

 

 

 

 

 

 

 

new t

 

 

X.h

 

ˆ =

 

 

 

 

 

 

 

 

 

 

 

h2

 

6.

Calculate the guessed x loadings by

 

 

 

 

 

 

 

 

 

 

 

t .X

 

pˆ =

 

ˆ

 

 

 

 

t2

 

 

 

 

ˆ

7.

Calculate the c loadings (a vector rather than scalar in PLS2) by

 

 

 

 

C .t

 

qˆ =

 

 

ˆ

 

 

 

 

t2

 

 

 

ˆ

8.

If this is the first iteration, remember the scores, and call them initial t, then produce

 

a new vector u by

 

 

C.qˆ

 

 

 

u

=

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

q2

and return to step 4.

Check for Convergence

9.If this is the second time round, compare the new and old scores vectors for

example, by looking at the size of the sum of square difference in the old and new scores, i.e. (initial tˆ − new tˆ)2. If this is small the PLS component has been

adequately modelled, set the PLS scores (t) and both types of loadings (p and c) for the current PC to tˆ, pˆ , and qˆ . Otherwise, calculate a new value of u as in step 8 and return to step 4.

Compute the Component and Calculate Residuals

10.Subtract the effect of the new PLS component from the data matrix to obtain a residual data matrix:

 

resid X = X t.p

11. Determine the new concentration estimate by

+

 

 

ˆ

 

=

 

 

ˆ

 

 

new C

 

initial C

 

t.q

and sum the contribution of all

components calculated to give an

estimated cˆ. Calculate

resid

C =

true

C

ˆ

 

 

 

 

 

 

 

 

C

Further PLS Components

12.If further components are required, replace both X and C by the residuals and return to step 3.

416

CHEMOMETRICS

 

 

A.2.4 Tri-linear PLS1

The algorithm below is based closely on PLS1 and is suitable when there is only one column in the c vector.

Initialisation

1.Take a three-way tensor Z and, if required, preprocess (e.g. mean centre or stan-

dardise) to give the tensor X which is used for PLS. Perform all preprocessing on this tensor. The tensor has dimensions I × J × K.

2.Preprocess the concentrations if appropriate to give a vector c.

New PLS Component

3. From the original tensor, create a new matrix H with dimensions J × K which is the sum of each of the I matrices for each of the samples multiplied by the concentration of the analyte for the relevant sample, i.e.

H = X1c1 + X2c2 + · · · + XI cI

or, as a summation

I

hjk = ci xijk i=1

4.Perform PCA on H to obtain the scores and loadings, h t and h p for the first PC of H. Note that only the first PC is retained, and for each new PLS component a fresh H matrix is obtained.

5.Calculate the two x loadings for the current PLS component of the overall dataset by normalising the scores and loadings of H, i.e.

j p = ht

ht2

k p = hp

hp2

(the second step is generally not necessary for most PCA algorithm as hp is usually normalised).

6. Calculate the overall scores by

J

K

 

ti =

xijk j pj k pk

j =1 k=1

7. Calculate the c loadings vector

q = (T .T )1.T .c

APPENDICES

417

 

 

where T is the scores matrix each column consisting of one component (a vector for the first PLS component).

Compute the Component and Calculate Residuals

8.Subtract the effect of the new PLS component from the original data matrix to obtain a residual data matrix (for each sample i):

resid

j k

 

Xi = Xi ti . p. p

9. Determine the new concentration estimates by

cˆ = T .q

Calculate

resid c = true c cˆ

Further PLS Components

10.If further components are required, replace both X and c by the residuals and return to step 3.

A.3 Basic Statistical Concepts

There are numerous texts on basic statistics, some of them oriented towards chemists. It is not the aim of this section to provide a comprehensive background, but simply to provide the main definitions and tables that are helpful for using this text.

A.3.1 Descriptive Statistics

A.3.1.1 Mean

The mean of a series of measurements is defined by

I

x = xi /I

i=1

Conventionally a bar is placed above the letter. Sometimes the letter m is used, but in this text we will avoid this, as m is often used to denote an index. Hence the mean of the measurements

4 8 5 6 2 5 6 0

is x = (4 + 8 + 5 6 + 2 5 + 6 + 0)/8 = 1.75.

Statistically, this sample mean is often considered an estimate of the true population mean sometimes denoted by µ. The population involves all possible samples, whereas only a selection are observed. In some cases in chemometrics this distinction is not so

418

CHEMOMETRICS

 

 

clear; for example, the mean intensity at a given wavelength over a chromatogram is a purely experimental variable.

A.3.1.2 Variance and Standard Deviation

The estimated or sample variance of a series of measurements is defined by

I

ν = (xi x)2/(I 1)

i=1

which can also be calculated using the equation

 

 

I

2

 

 

 

 

 

2

 

 

 

ν

=

 

/(I 1)

×

 

1

xi

I /(I

 

 

x

 

)

 

 

i=1

 

 

 

 

So the variance of the data in Section A.3.1.1 is

ν = (42 + 82 + 52 + 62 + 22 + 52 + 62 + 02)/7 1.752 × 8/7 = 25.928

This equation is useful when it is required to estimate the variance from a series of samples. However, the true population variance is defined by

I I

ν = (xi x)2/I = xi2/I x2

i=1 i=1

The reason why there is a factor of I 1 when using measurements in a number of samples to estimate statistics is because one degree of freedom is lost when determining variance experimentally. For example, if we record one sample, the sum of squares

I=1 (xi x)2 must be equal to 0, but this does not imply that the variance of the

i

parent population is 0. As the number of samples increases, this small correction is not very important, and sometimes ignored.

The standard deviation, s, is simply the square root of the variance. The population standard deviation is sometimes denoted by σ .

In chemometrics it is usual to use the population and not the sample standard deviation for standardising a data matrix. The reason is that we are not trying to estimate parameters in this case, but just to put different variables on a similar scale.

A.3.1.3 Covariance and Correlation Coefficient

The covariance between two variables is a method for determining how closely they follow similar trends. It will never exceed in magnitude the geometric mean of the variance of the two variables; the lower is the value, the less close are the trends. Both variables must be measured for an identical number of samples, I in this case. The sample or estimated covariance between variables x and y is defined by

I

covxy = (xi x)(yi y)/(I 1)

i=1

APPENDICES

419

 

 

whereas the population statistic is given by

I

covxy = (xi x)(yi y)/I

i=1

Unlike the variance, it is perfectly possible for a covariance to take on negative values. Many chemometricians prefer to use the correlation coefficient, given by

r

 

 

 

I

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

(xi

 

 

 

 

 

xy =

covxy

=

 

 

i=1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

sx .sy

 

 

 

 

 

 

 

 

 

 

I

(xi

 

x)2

I

(yi

 

 

y)2

 

 

 

 

i

 

 

 

i

1

 

 

1

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

=

 

 

 

 

=

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Note that the definition of the correlation coefficient is identical both for samples and populations.

The correlation coefficient has a value between 1 and +1. If close to +1, the two variables are perfectly correlated. In many applications, correlation coefficients of 1 also indicate a perfect relationship. Under such circumstances, the value of y can be exactly predicted if we know x. The closer the correlation coefficients are to zero, the harder it is to use one variable to predict another. Some people prefer to use the square of the correlation coefficient which varies between 0 and 1.

If two columns of a matrix have a correlation coefficient of ±1, the matrix is said to be rank deficient and has a determinant of 0, and so no inverse; this has consequences both in experimental design and in regression. There are various ways around this, such as by removing selected variables.

In some areas of chemometrics we used a variance–covariance matrix. This is a square matrix, whose dimensions usually equal the number of variables in a dataset, for example, if there are 20 variables the matrix has dimensions 20 × 20. The diagonal elements equal the variance of each variable and the off-diagonal elements the covariances. This matrix is symmetric about the diagonal. It is usual to employ population rather than sample statistics for this calculation.

A.3.2 Normal Distribution

The normal distribution is an important statistical concept. There are many ways of introducing such distributions. Many texts use a probability density function

 

=

σ

2π

 

2

σ

 

 

f (x)

 

 

1

exp

1

 

x µ

 

2

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

This rather complicated equation can be interpreted as follows. The function f (x) is proportional to the probability that a measurement has a value x for a normally distributed population of mean µ and standard deviation σ . The function is scaled so that the area under the normal distribution curve is 1.

420

CHEMOMETRICS

 

 

Table A.1 Cumulative standardised normal distribution.

 

 

Values of cumulative probability for a given number of standard deviations from the mean.

 

 

 

0.0

0.00

 

0.01

 

0.02

 

0.03

 

0.04

 

0.05

 

0.06

 

0.07

 

0.08

 

0.09

 

 

0.500

00

0.503

99

0.507

98

0.511

97

0.515

95

0.519

94

0.523

92

0.527

90

0.531

88

0.535

86

 

0.1

0.539

83

0.543

80

0.547

76

0.551

72

0.555

67

0.559

62

0.563

56

0.567

49

0.571

42

0.575

35

 

0.2

0.579

26

0.583

17

0.587

06

0.590

95

0.594

83

0.598

71

0.602

57

0.606

42

0.610

26

0.614

09

 

0.3

0.617

91

0.621

72

0.625

52

0.629

30

0.633

07

0.636

83

0.640

58

0.644

31

0.648

03

0.651

73

 

0.4

0.655

42

0.659

10

0.662

76

0.666

40

0.670

03

0.673

64

0.677

24

0.680

82

0.684

39

0.687

93

 

0.5

0.691

46

0.694

97

0.698

47

0.701

94

0.705

40

0.708

84

0.712

26

0.715

66

0.719

04

0.722

40

 

0.6

0.725

75

0.729

07

0.732

37

0.735

65

0.738

91

0.742

15

0.745

37

0.748

57

0.751

75

0.754

90

 

0.7

0.758

04

0.761

15

0.764

24

0.767

30

0.770

35

0.773

37

0.776

37

0.779

35

0.782

30

0.785

24

 

0.8

0.788

14

0.791

03

0.793

89

0.796

73

0.799

55

0.802

34

0.805

11

0.807

85

0.810

57

0.813

27

 

0.9

0.815

94

0.818

59

0.821

21

0.823

81

0.826

39

0.828

94

0.831

47

0.833

98

0.836

46

0.838

91

 

1.0

0.841

34

0.843

75

0.846

14

0.848

49

0.850

83

0.853

14

0.855

43

0.857

69

0.859

93

0.862

14

 

1.1

0.864

33

0.866

50

0.868

64

0.870

76

0.872

86

0.874

93

0.876

98

0.879

00

0.881

00

0.882

98

 

1.2

0.884

93

0.886

86

0.888

77

0.890

65

0.892

51

0.894

35

0.896

17

0.897

96

0.899

73

0.901

47

 

1.3

0.903

20

0.904

90

0.906

58

0.908

24

0.909

88

0.911

49

0.913

08

0.914

66

0.916

21

0.917

74

 

1.4

0.919

24

0.920

73

0.922

20

0.923

64

0.925

07

0.926

47

0.927

85

0.929

22

0.930

56

0.931

89

 

1.5

0.933

19

0.934

48

0.935

74

0.936

99

0.938

22

0.939

43

0.940

62

0.941

79

0.942

95

0.944

08

 

1.6

0.945

20

0.946

30

0.947

38

0.948

45

0.949

50

0.950

53

0.951

54

0.952

54

0.953

52

0.954

49

 

1.7

0.955

43

0.956

37

0.957

28

0.958

18

0.959

07

0.959

94

0.960

80

0.961

64

0.962

46

0.963

27

 

1.8

0.964

07

0.964

85

0.965

62

0.966

38

0.967

12

0.967

84

0.968

56

0.969

26

0.969

95

0.970

62

 

1.9

0.971

28

0.971

93

0.972

57

0.973

20

0.973

81

0.974

41

0.975

00

0.975

58

0.976

15

0.976

70

 

2.0

0.977

25

0.977

78

0.978

31

0.978

82

0.979

32

0.979

82

0.980

30

0.980

77

0.981

24

0.981

69

 

2.1

0.982

14

0.982

57

0.983

00

0.983

41

0.983

82

0.984

22

0.984

61

0.985

00

0.985

37

0.985

74

 

2.2

0.986

10

0.986

45

0.986

79

0.987

13

0.987

45

0.987

78

0.988

09

0.988

40

0.988

70

0.988

99

 

2.3

0.989

28

0.989

56

0.989

83

0.990

10

0.990

36

0.990

61

0.990

86

0.991

11

0.991

34

0.991

58

 

2.4

0.991

80

0.992

02

0.992

24

0.992

45

0.992

66

0.992

86

0.993

05

0.993

24

0.993

43

0.993

61

 

2.5

0.993

79

0.993

96

0.994

13

0.994

30

0.994

46

0.994

61

0.994

77

0.994

92

0.995

06

0.995

20

 

2.6

0.995

34

0.995

47

0.995

60

0.995

73

0.995

85

0.995

98

0.996

09

0.996

21

0.996

32

0.996

43

 

2.7

0.996

53

0.996

64

0.996

74

0.996

83

0.996

93

0.997

02

0.997

11

0.997

20

0.997

28

0.997

36

 

2.8

0.997

44

0.997

52

0.997

60

0.997

67

0.997

74

0.997

81

0.997

88

0.997

95

0.998

01

0.998

07

 

2.9

0.998

13

0.998

19

0.998

25

0.998

31

0.998

36

0.998

41

0.998

46

0.998

51

0.998

56

0.998

61

 

3.0

0.0

 

0.1

 

0.2

 

0.3

 

0.4

 

0.5

 

0.6

 

0.7

 

0.8

 

0.9

 

 

0.998

65

0.999

03

0.999

31

0.999

52

0.999

66

0.999

77

0.999

84

0.999

89

0.999

93

0.999

95

 

4.0

0.999

968

0.999

979

0.999

987

0.999

991

0.999

995

0.999

997

0.999

998

0.999

999

0.999

999

1.000

000

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Most tables deal with the standardised normal distribution. This involves first standardising the raw data, to give a new value z, and the equation simplifies to

1

exp

z2

 

f (z) =

 

 

2

2π

Instead of calculating f (z), most people

look at

the area under the normal distri-

bution curve. This is proportional to the probability that a measurement is between certain limits. For example the probability that a measurement is between one and two

APPENDICES

421

 

 

standard deviations can be calculated by taking the proportion of the overall area for which 1 z 2.

These numbers can be obtained using simple functions, e.g. in a spreadsheet, but are often conventionally presented in tabular form. There are a surprisingly large number of types of tables, but Table A.1 allows the reader to calculate relevant information. This table is of the cumulative normal distribution, and represents the area to the left of the curve for a specified number of standard deviations from the mean. The number of standard deviations equals the sum of the left-hand column and the top row, so, for example, the area for 1.17 standard deviations equals 0.879 00.

Using this table it is then possible to determine the probability of a measurement between any specific limits.

The probability that a measurement is above 1 standard deviation from the mean is equal to 1 0.841 34 = 0.158 66.

The probability that a measurement is more than 1 standard deviation from the mean will be twice this, because both positive and negative deviations are possible and

the curve is symmetrical, and is equal to 0.317 32. Put another way, around a third of all measurements will fall outside 1 standard deviation from the mean.

The probability that a measurement falls between 2 and +1 standard deviations from the mean can be calculated as follows:

the probability that a measurement falls between 0 and 2 standard deviations is the same as the probability it falls between 0 and +2 standard deviations and is equal to 0.977 25 0.5 = 0.477 25;

the probability that a measurement falls between 0 and +1 standard deviations is equal to 0.841 34 0.5 = 0.341 34;

therefore the total probability is 0.477 25 + 0.341 34 = 0.818 59.

The normal distribution curve is not only a probability distribution but is also used to describe peakshapes in spectroscopy and chromatography.

A.3.3 F Distribution

The F -test is normally used to compare two variances or errors and ask either whether one variance is significantly greater than the other (one-tailed) or whether it differs significantly (two-tailed). In this book we use only the one-tailed F -test, mainly to see whether one error (e.g. lack-of-fit) is significantly greater than a second one (e.g. experimental or analytical).

The F statistic is the ratio between these two variances, normally presented as a number greater than 1, i.e. the largest over the smallest. The F distribution depends on the number of degrees of freedom of each variable, so, if the highest variance is obtained from 10 samples, and the lowest from seven samples, the two variables have nine and six degrees of freedom, respectively. The F distribution differs according to the number of degrees of freedom, and it would be theoretically possible to produce an F distribution table for every possible combination of degrees of freedom, similar to the normal distribution table. However, this would mean an enormous number of tables (in theory an infinite number), and it is more usual simply to calculate the F statistic at certain well defined probability levels.

A one-tailed F statistic at the 1 % probability level is the value of the F ratio above which only 1 % of measurements would fall if the two variances were not significantly

422

CHEMOMETRICS

 

 

Table A.2 One-tailed F distribution at the 1 % level.

6365.59

99.4987

26.1252

13.4633

9.0204

6.8801

5.6496

4.8588

4.3106

3.9090

3.6025

3.3608

3.1654

3.0040

2.8684

2.7528

2.6531

2.5660

2.4893

2.4212

2.1694

2.0062

1.8910

1.8047

1.7374

1.6831

1.4273

1.0000

100

6333.92

99.4914

26.2407

13.5769

9.1300

6.9867

5.7546

4.9633

4.4150

4.0137

3.7077

3.4668

3.2723

3.1118

2.9772

2.8627

2.7639

2.6779

2.6023

2.5353

2.2888

2.1307

2.0202

1.9383

1.8751

1.8248

1.5977

1.3581

50

6302.26

99.4769

26.3544

13.6897

9.2377

7.0914

5.8577

5.0654

4.5167

4.1155

3.8097

3.5692

3.3752

3.2153

3.0814

2.9675

2.8694

2.7841

2.7092

2.6430

2.3999

2.2450

2.1374

2.0581

1.9972

1.9490

1.7353

1.5231

30

6260.35

99.4660

26.5045

13.8375

9.3794

7.2286

5.9920

5.1981

4.6486

4.2469

3.9411

3.7008

3.5070

3.3476

3.2141

3.1007

3.0032

2.9185

2.8442

2.7785

2.5383

2.3860

2.2806

2.2034

2.1443

2.0976

1.8933

1.6964

25

6239.86

99.4587

26.5791

13.9107

9.4492

7.2960

6.0579

5.2631

4.7130

4.3111

4.0051

3.7647

3.5710

3.4116

3.2782

3.1650

3.0676

2.9831

2.9089

2.8434

2.6041

2.4526

2.3480

2.2714

2.2129

2.1667

1.9651

1.7726

20

6208.66

99.4478

26.6900

14.0194

9.5527

7.3958

6.1555

5.3591

4.8080

4.4054

4.0990

3.8584

3.6646

3.5052

3.3719

3.2587

3.1615

3.0771

3.0031

2.9377

2.6993

2.5487

2.4448

2.3689

2.3109

2.2652

2.0666

1.8783

15

6156.97

99.4332

26.8719

14.1981

9.7223

7.5590

6.3144

5.5152

4.9621

4.5582

4.2509

4.0096

3.8154

3.6557

3.5222

3.4090

3.3117

3.2273

3.1533

3.0880

2.8502

2.7002

2.5970

2.5216

2.4642

2.4190

2.2230

2.0385

10

6055.93

99.3969

27.2285

14.5460

10.0511

7.8742

6.6201

5.8143

5.2565

4.8491

4.5393

4.2961

4.1003

3.9394

3.8049

3.6909

3.5931

3.5081

3.4338

3.3682

3.1294

2.9791

2.8758

2.8005

2.7432

2.6981

2.5033

2.3209

9

6022.40

99.3896

27.3449

14.6592

10.1577

7.9760

6.7188

5.9106

5.3511

4.9424

4.6315

4.3875

4.1911

4.0297

3.8948

3.7804

3.6823

3.5971

3.5225

3.4567

3.2172

3.0665

2.9630

2.8876

2.8301

2.7850

2.5898

2.4073

8

5980.95

99.3750

27.4895

14.7988

10.2893

8.1017

6.8401

6.0288

5.4671

5.0567

4.7445

4.4994

4.3021

4.1400

4.0044

3.8896

3.7909

3.7054

3.6305

3.5644

3.3239

3.1726

3.0687

2.9930

2.9353

2.8900

2.6943

2.5113

7

5928.33

99.3568

27.6714

14.9757

10.4556

8.2600

6.9929

6.1776

5.6128

5.2001

4.8860

4.6395

4.4410

4.2779

4.1416

4.0259

3.9267

3.8406

3.7653

3.6987

3.4568

3.3045

3.1999

3.1238

3.0658

3.0202

2.8233

2.6393

6

5858.95

99.3314

27.9106

15.2068

10.6722

8.4660

7.1914

6.3707

5.8018

5.3858

5.0692

4.8205

4.6203

4.4558

4.3183

4.2016

4.1015

4.0146

3.9386

3.8714

3.6272

3.4735

3.3679

3.2910

3.2325

3.1864

2.9877

2.8020

5

5763.96

99.3023

28.2371

15.5219

10.9671

8.7459

7.4604

6.6318

6.0569

5.6364

5.3160

5.0644

4.8616

4.6950

4.5556

4.4374

4.3360

4.2479

4.1708

4.1027

3.8550

3.6990

3.5919

3.5138

3.4544

3.4077

3.2059

3.0172

4

5624.26

99.2513

28.7100

15.9771

11.3919

9.1484

7.8467

7.0061

6.4221

5.9944

5.6683

5.4119

5.2053

5.0354

4.8932

4.7726

4.6689

4.5790

4.5002

4.4307

4.1774

4.0179

3.9082

3.8283

3.7674

3.7195

3.5127

3.3192

3

5403.53

99.1640

29.4567

16.6942

12.0599

9.7796

8.4513

7.5910

6.9920

6.5523

6.2167

5.9525

5.7394

5.5639

5.4170

5.2922

5.1850

5.0919

5.0103

4.9382

4.6755

4.5097

4.3958

4.3126

4.2492

4.1994

3.9837

3.7816

2

4999.34

99.0003

30.8164

17.9998

13.2741

10.9249

9.5465

8.6491

8.0215

7.5595

7.2057

6.9266

6.7009

6.5149

6.3588

6.2263

6.1121

6.0129

5.9259

5.8490

5.5680

5.3903

5.2679

5.1785

5.1103

5.0566

4.8239

4.6052

1

4052.18

98.5019

34.1161

21.1976

16.2581

13.7452

12.2463

11.2586

10.5615

10.0442

9.6461

9.3303

9.0738

8.8617

8.6832

8.5309

8.3998

8.2855

8.1850

8.0960

7.7698

7.5624

7.4191

7.3142

7.2339

7.1706

6.8953

6.6349

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