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Memo to Greg Vaughn -2- 1 June 1989 <br /> (Freon 113) , 1,1 ,1-trichloroethane (TCA) and tetrachloroethylene (PCE) . Each <br /> of these constituents were in concentrations an order of magnitude lower than <br /> their respective MCL or SAL. <br /> Based on these results, the drummed purge water meets drinking water standards <br /> and therefore, may be disposed of to land without posing a threat to water <br /> quality. The drilling muds and cuttings are not hazardous. However, the <br /> reported concentrations of heavy metals were for totals and a determination of <br /> a potential threat to water quality is more difficult. In those cases where land <br /> disposal is proposed. Future sample analyses of the drilling muds and cuttings <br /> should be performed using the Waste Extraction Test using a citrate buffer as <br /> described in Section 66700 of Title 22 of the Health and Safety Code. If the <br /> total concentration for heavy metals are assumed to be representative of worst <br /> case soluble concentrations, then a ten-fold dilution factor is used in the <br /> conversion from mg/kg to mg/1 . Using the Designated Methodology an attenuation <br /> factor must be considered to determine the potential threat to water quality. <br /> If an attenuation factor of 10 is used, then only four constituents (arsenic, <br /> barium, chromium and lead) , when compared to the respective Drinking Water <br /> Standard (DWS) , are greater than that concentration. However, if an attenuation <br /> factor of 100 is used, then all the heavy metal constituents, when compared, are <br /> below their respective DWS. (Refer to the attached Table. ) These considerations <br /> are also applicable to the VOCs detected in the muds and cuttings. TCE was the <br /> only VOC that would not be below the DWS using an attenuation factor of 10 but <br /> would be below the DWS using an attenuation factor of 100. If the volumes to <br /> be disposed, disposal areas, disposal method, soil/sediment soils at the facility <br /> are considered to influence the attenuation, it is my opinion that a one time, <br /> short-term application for disposal to land of these muds and cuttings should <br /> not pose a threat to water quality. <br /> The second document: Drilling Mud, Cuttings, and Development Water Disposal , <br /> was submitted by Hargis and Associates and contained three separate proposals <br /> for handling the wastes. Hargis has proposed to land dispose on-site of muds <br /> and cuttings which have concentrations of VOCs below the STLC or TTLC. However, <br /> relatively few VOCs (TCE, vinyl chloride) have an established STLC or TTLC <br /> values. Hargis has proposed to land dispose of VOC contaminated muds or cuttings <br /> which may be considered to be at designated levels. This proposal is not <br /> acceptable. The Hargis proposal is also unacceptable in that they did not <br /> include sampling and analyses for heavy metals. <br /> Hargis has proposed that muds or cuttings which exceed the STLC or TTLC will be <br /> hauled to an appropriate facility for disposal . They also proposed to dispose <br /> of any development waters which exceed the MCL or SAL at an appropriate facility. <br /> The latter two proposals are acceptable provided those facilities are permitted <br /> to accept those types of wastes. <br />