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Kennedy/Jenks/Chilton <br /> Mr. John Menke <br /> California Regional Water Quality Control Board <br /> 30 November 1989 <br /> Page 3 <br /> fuel storage tank. The remaining 4 borings and 3 monitoring wells did not <br /> indicated that petroleum hydrocarbons were of a concern. Although other <br /> potential contamination sources exist near the Cal -Farm Supply Facility <br /> (Pacific Molasses and Port of Stockton) the results of the Preliminary Site <br /> Investigation did not indicate that these sites have contributed to the <br /> problem previously detected at the site. <br /> Task 4 is additional soil sampling to determine the extent of DDT contaminated <br /> soil . The described sampling procedure is satisfactory, but you may wish to <br /> decrease the number of sampling points south of the facility fence and conduct <br /> some sampling at depth in the areas of known contamination in order to <br /> estimated the volume of soil needing treatment or removal . I note that you <br /> are proposing 1 ppm as a cleanup level as discussed in 14 July 1989 <br /> Preliminary Site Investigation Report (page 7, last paragraph) . As noted in <br /> the Report, the TTLC is not an action level ; however, the TTLC level of 1 ppm <br /> is often proposed as cleanup goal . A more appropriate method of setting goals <br /> is to consider potential health effects, routes of exposure, and probable <br /> attenuation. Such a process results in a site specific level that usually <br /> considers current and potential site use. By applying such a process to the <br /> Cal-Farm Supply site, you may be able to justify the proposed 1 ppm level . <br /> Until the site is fully characterized, I cannot validate the 1 ppm level as <br /> adequate to protect water quality, but I expect that it will be acceptable. <br /> Likewise, other pesticide residues at the site should be reviewed and cleanup <br /> levels determined. The process of calculating cleanup levels based on <br /> toxicities relative to the TTLC for DDT does not result in satisfactory goals <br /> because no consideration is given to relative mobility and appropriate <br /> toxicity (the TTLC for DDT was based on cumulative toxicity to fish) . Based <br /> on my review of the pesticide levels determined to date, I do not anticipate <br /> that any other pesticide at the site will displace DDT as the focus for <br /> cleanup activities (i .e. , if soils are remediated to address concerns for DDT, <br /> no additional soil remediation will be necessary for other pesticides) . <br /> A clean-up level of 1 ppm was proposed for the Cal -Farm Supply Stockton <br /> Facility so that soils which contain chemicals at concentrations which the <br /> State of California considers hazardous (CCR Title 22) would be removed from <br /> the site. The EPA, in it's RCRA Facility Investigation (RFI) document (530/ <br /> SW-89-031) proposes a health-based action level of 2.1 ppm for DDT in soil <br /> based on oral exposure. Site specific information such as dominant site <br /> lithology, the low mobility of DDT in the environment, and the depth to <br /> groundwater at the site would likely cause this number to rise if a risk <br /> assessment was conducted for the Cal -Farm Supply Stockton Facility. However, <br /> Cal -Farm Supply wishes to remove soil containing concentrations of DDT which <br /> exceed 1 ppm, therefore, a risk assessment was not deemed necessary. <br /> Task 5 is disposal of soil containing DDT. Whereas DDT is a "soft-hammer" land <br /> ban waste, it will be necessary to demonstrate that no treatment process is <br />