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A number of methods can be used to permit statistical comparisons of
censored data, including simple substitution, uniform distribution substitution,
maximum likelihood, and regression methods. Based on the results of a
simulation study conducted to identify which of 10 censored data methods work
best to maintain power and minimize Type I error rate in LSD comparisons when
n is small, Clarke (1998) recommended the use of nonparametric tests. A
constant lower than all reported values, such as zero, one-half DL, or negative
DL, is assigned to all nondetects and then the data are converted to rankits or
ranks prior to running a t-test or LSD test, or Dunn=s Test may be performed.
The power of any test will generally decline as the amount of censoring
increases; statistical analysis is not recommended when more than 60 to 80
percent of the data are nondetects. Deletion of nondetects is not recommended
as it results in excessive loss of information and power as amount of censoring
increases.
L.3.2.2 Comparison with an action level
In this comparison, the objective is to determine whether the mean bio-
accumulation of contaminants in plants or animals exposed to a dredged material
is significantly less than a specified action level or standard. If the mean tissue
concentration of one or more contaminants of concern is greater than or equal to
the applicable action level, then no statistical testing is required. If the mean
tissue concentrations of a contaminant of concern are less than the applicable
action level, then a confidence-interval approach is used to determine if these
means are significantly less than the action level. One-sided tests are appropriate
since there is concern only if bioaccumulation from the dredged material is not
significantly less than the action level. There are two different approaches to
conducting these tests, and both are acceptable.
The first approach is to calculate a value of t, much as in a t-test (this
approach is often called a one-sample t-test):
x - action level
t=
(L-25)
2
s /n
where x, s2, and n refer to mean, variance, and number of replicates for
-
contaminant bioaccumulation from the dredged material.
If tests of equality of variances in the comparison of dredged materials with
the reference indicate that variances are equal for all treatments, then MSE from
the ANOVA is used as s2, and calculated t is compared to t0.95, with N - k degrees
of freedom. If the variances are not equal, then s2 for the individual treatment is
used, and calculated t compared with t0.95, with n - 1 degrees of freedom. If the
data were transformed to normalize the distributions or equalize variances, then
all calculations should be carried out on transformed values.
Another approach is to calculate the upper one-sided 95 percent confidence
limit (UCL), and compare it to the action level:
L36
Appendix L Selected Resource Documents
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