1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
1.1 MB pdf - Bolsa Chica Lowlands Restoration Project
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SECTION 3: ANALYSIS<br />
dredge footprint) were grouped together. (The analytical results from the Focused Sampling<br />
and Analyses and the Tetra Tech Phase II sampling were not included in the development<br />
of the background values). Using samples from potentially contaminated areas (i.e., focused<br />
sites) is reasonable because even if the samples have been contaminated with one or more<br />
metals, they may still have background levels for a number of other metals (Cal/EPA, 1997).<br />
The reported analytical values for all samples that were considered as non-detects (i.e., those<br />
results accompanied by the laboratory flag “U” or "UJ") were evaluated at one-half the<br />
reporting limit. All other laboratory results were left unchanged. This transformed data set<br />
was then plotted in a manner similar to the method for displaying analytical data shown in<br />
the Cal/EPA (1997) guidance for evaluating inorganic constituents. The transformed data<br />
were sorted in order of ascending concentration for each metal and plotted against the<br />
cumulative percent of samples. The cumulative percent plots for selected inorganic<br />
constituents are included in Appendix E. Where available, sediment screening benchmark<br />
values (Low and Median Effect Range [ER-L and ER-M] after Long et al., 1995 and other<br />
sources) are also provided on the cumulative percent plots for comparative purposes.<br />
When inorganics are measured for a relatively large number of background or site soils, the<br />
plotted cumulative percent curves describe a distribution of the sample results. When only<br />
a few data points are available, the distributions of inorganic levels are more difficult to<br />
describe and often only the central tendency may be described with confidence. When<br />
large data sets are available, the extremes of distribution are more easily characterized.<br />
Depending on the size of the background sample data set, an upper percentile (e.g., 95th<br />
or 99th) might be considered an appropriate criterion for the upper range of background<br />
conditions (Cal/EPA, 1997).<br />
To estimate the background levels for selected metals, each of the cumulative percent plots<br />
was examined for certain characteristics as described in Appendix E. For most metals, nondetected<br />
sample data were kept within the data sets although these data were represented<br />
as one-half the reporting limit. There were only five metals for which the nondetects<br />
appeared to significantly affect the cumulative distributions (see text below). The estimated<br />
break point between the background and apparently elevated concentrations for the three<br />
sample groups (all sample, surface, and subsurface) of each element, along with the<br />
percentile values and sample size summary, are presented in Table 3-10. Although the<br />
background evaluation results for all three groups are presented, the estimated background<br />
level for each of the selected inorganics was consistently taken from the all sample group.<br />
The percentile values corresponding to the break point values are reported in Table 3-10 but<br />
the percentile values were not used as a selection criterion for the break point.<br />
In addition to the short descriptions of background levels given below for the selected<br />
inorganics, selected cumulative percent plots are also included to illustrate how the<br />
background levels were determined. Figure 3-4 shows the cumulative percent curve for<br />
copper, with an arrow showing the break point for the distribution of sample concentrations<br />
for this constituent. Break points were chosen in a similar manner for the other selected<br />
inorganic constituents where the cumulative percent distribution shows a distinct point<br />
where a marked slope increase was noted.<br />
SAC/143368(003.DOC) 3-13 ERA REPORT<br />
7/31/02