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1993, the parties to the FFA have agreed to clarify the objectives of the original <br /> work plan in this Amendment. Therefore: <br /> • Please include a new section in the Work Plan Addendum which restates the <br /> sampling objectives of the various phases. In particular, with regard to Phase <br /> I sampling, insert text which states "It is not the intent of Phase I sampling to <br /> 'deselect'potential source areas from further investigation. Instead, conclusions to <br /> cease further investigation, out a source by source basis, will be made via consensus <br /> of the parties to the Federal Facility Agreement (FFA)." <br /> Sections 3.1.2.3 and 3.1.2.4 of the Comprehensive Work Plan assert an intent to apply <br /> statistical tests to all data used as Phase I data.1 <br /> 5. Background concentrations for arsenic at DDRW-Sharpe (10 to 15 miles from <br /> DDRW-Tracy) are discussed in these amendments as if these same background <br /> concentrations for arsenic were appropriate for DDRW-Tracy. However, no <br /> rationale is presented to support this conclusion. Neither the U.S. Geological Survcy <br /> article (Dubrovsky et al., 1991), nor the 1991-1992 well monitoring data (filtered or <br /> dissolved arsenic) from both Woodward-Clyde Consultants (WCC) and James M. <br /> Montgomery (JMM) at DDRW-Tracy (see the attached Table 1) suggest that there <br /> exists high background concentrations for arsenic. (JMM's non-turbid total metals <br /> data from September 1992 gives total arsenic concentrations only slightly higher <br /> than corresponding dissolved concentrations of arsenic.) Risk Assessment Guidance <br /> for Stuperfund (Part A; RAGS, 1989) states in part in Section 4.4.2 on page No. 4-8 <br /> that "background samples are collected at or near the hazardous waste site in areas not <br /> influenced by site contamination . . . the locations of background samples must be areas <br /> that could not have received contamination from the site, but that do have the same basic <br /> 1 If DDRW-tract' were to desire to eliminate sites from further consideration, EPA <br /> would likely require statistical tests to assure adequate sampling. These statistical tests arc <br /> designed to determine whether or not further sampling is required and if additional <br /> samples are required per site. Under one hypothetical scenario (developed by WCC), no <br /> further samples would be required at some particular sites; the reason for this is that the <br /> statistical tests (after Phase I sampling) would indicate that enough samples were already <br /> taken, and that no appreciable risks exist at those sites to human health and/or the <br /> environment. This is a possibility at some sites. At most sites, however, it is expected that <br /> more samples will be required to state with statistical confidence that there exists or does <br /> not exist, risk. For locations where only one boring/monitoring well are to be analyzed in <br /> Phase I (SWMU Nos. 20, 21, 23, 24, and 27) data may be insufficient to determine "no risk." <br /> For three other sites (SWMU Nos. 6, 14, 15) in which the number has been reduced from 3 to <br /> 2 samples; it is uncertain how the statistical test will be successfully applied. Other sites <br /> which possibly may have insufficient samples to allow "deselection" are SWMU Nos. 3 <br /> (IWPs), 33 (IWPL), and burn pit SWMUs Nos. 7, 8, and 16. These latter SWMUs are <br /> heterogenous and known to contain, or expected to contain, wide ranges of hazardous waste <br /> constituents. <br /> USEPA/R9 12 Apr 93 2/19 <br />