Environmental Engineering Reference
In-Depth Information
Table 1.17
Numbers of data points with bivar
i
ate information
Y
1
Y
2
Y
3
Y
4
Y
5
Y
6
Y
7
Y
8
Y
9
Y
10
OCR
Y
1
3822 3822 3412 2084 1362 1835 1184 680 618 541 1475
Y
2
4265 3424 2169 1433 2173 1203 688 626 549 1745
Y
3
Index properties 3661 1999 1314 1709 1279
660 598 521 1388
Y
4
3370 1944 2419 853 965 862 668 1959
Y
5
2028 1423 554 780 691 543 1984
Y
6
3532 715 595 533 525 2120
Y
7
Stresses and strengths 1589 240 230 190
586
Y
8
1016 862 668 832
Y
9
Symmetry 862 590 692
Y
10
CPTU parameters 668
544
OCR 3531
Source: Ching, J. and Phoon, K.K. 2014b.
Canadian Geotechnical Journal
, 51(6), 686-704, reproduced with permission of the
NRC Research Press.
1.7.2 Construction of multivariate distribution
The multivariate non-normal distribution for (Y
1
, Y
2
, …, Y
10
) is constructed using the
approach discussed in Section 1.6: (1) Fit a Johnson distribution to each component (Yi),
i
), (2)
convert Y
i
into standard normal Xi
i
, and (3) compute the correlation matrix for (X
1
, X
2
, …,
X
10
). The key challenge is to compute a valid
positive-definite
correlation matrix in step (3).
As discussed in Section 1.4.3, the correlation matrix is guaranteed to be at least semiposi-
tive definite if it is estimated from multivariate data
(
Equation 1.57
)
. However, multivariate
data are rare in geotechnical engineering. The practical approach is to estimate each entry
in the correlation separately from
bivariate
data
(
Equation 1.58
)
. The downside is that such
a piecemeal approach will not guarantee a positive-definite correlation matrix. This rather
abstract theoretical property cannot be dismissed without running the risk of producing
completely absurd answers such as a negative variance as shown in Section 1.4.3. This sec-
tion demonstrates how a correlation matrix can be estimated from actual bivariate data
while preserving the critical property of positive definiteness.
1.7.2.1 Fit a Johnson distribution to each component (Yi)
i
)
Each component (Y
i
) can be fitted to a Johnson distribution using the procedures introduced
in Section 1.6.3. The distribution type and parameters are summarized in
Table 1.18
.
1.7.2.2 Convert Y
i
into standard normal Xi
i
It is easy to transform the soil parameters into standard normal random variables (X
1
, X
2
,
Table 1.18
. The normality of this transformed data can be checked using a probability plot
or the K-S test. Using MATLAB function kstest, the
p
-values associated with the K-S test
are five
p
-values <0.05 (X
1
, X
2
, X
3
, X
6
, X
7
), indicating that there is sufficient evidence to
reject the null hypothesis that Xi
i
is a standard normal random variable at a level of sig-
nificance of 5%. However, the Johnson distribution is still adopted in the ensuing analysis
because of its analytical elegance (discussed later).
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