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 />
questionable. The use of other confirmation techniques, such as gas<br />
chromatography/mass spectroscopy should be considered in the future.<br />
The validated data from the ERA chemical database (including both Tetra Tech and<br />
CH2M HILL samples) were then evaluated for their use in the risk assessment. Data were<br />
retained or eliminated from the ERA database using the following guidelines:<br />
• Media included in the database consisted of field-collected sediment/soil, surface water,<br />
and biological tissue (terrestrial plants, terrestrial and aquatic invertebrates, fish, stilt eggs,<br />
and small mammals) and polychaete worm tissues from the bioaccumulation studies.<br />
• Focused and random sampling sites were included in the database for purposes of data<br />
summarization and to evaluate exposure point concentrations. Data from the dredge<br />
sampling (both surface and deep samples) were also included for purposes of evaluating<br />
site-specific background concentrations (see Section 3.1.3); however, only those data that<br />
were collected from the 0- to 2-foot depth after habitat restoration were included in the<br />
data used for exposure and effects evaluations.<br />
• Chemical results with final validation qualifiers of any letter except "U" or "UJ" were<br />
considered detected.<br />
• Chemical results with final validation qualifiers of "U" (nondetect level or sample<br />
quantitation limit) or "UJ" (estimated nondetect level) were considered nondetects and<br />
were evaluated at one-half the sample-specific reporting limit to calculate summary<br />
statistics and exposure point concentrations. It should be noted that the Tetra Tech data<br />
did not include sample-specific reporting limits. If a chemical was nondetect, then the<br />
value reported was “0.” This resulted in a slight underestimation of some statistical<br />
parameters (e.g., mean and 95th UCL) as a “0” was evaluated rather than one-half of a<br />
small value. (For example, if the sample-specific reporting limit was 0.6, but a 0 was<br />
reported, then the value used in the summary statistics would have been 0 instead of<br />
0.3 [one-half of 0.6]).<br />
• Chemical results with a laboratory or validation qualifier of "R" were considered rejected<br />
and were removed from the database.<br />
• Chemical data for abiotic media were retained for all sampling locations within a<br />
given evaluation area if the chemical was detected at least once in a specific medium.<br />
Chemicals that were never detected in a specific medium were considered not present<br />
and were removed from the database. For example, if chemical “x” was detected in at<br />
least one sediment/soil sample in the Full Tidal area, then chemical “x” sediment/soil<br />
data from all sampling locations were retained. If chemical “x” was not detected in any<br />
of the surface water sampling locations, then it was assumed that chemical “x” was not<br />
present in surface water and all associated data were removed from the database.<br />
• Chemical data for biological media (i.e. tissue) were retained for all sampling locations<br />
If the chemical was detected once within the entire <strong>Lowlands</strong>. Data were not removed<br />
based on detection/non-detection within an evaluation area because tissue data were<br />
used to calculate bioaccumulation factors for the entire <strong>Lowlands</strong>.<br />
ERA REPORT 3-8 SAC/143368(003.DOC)<br />
7/31/02