Laserfiche WebLink
Antonia Vorster -2- 21 October 1987 <br /> To assess the above items a ground water monitoring program is recommended. <br /> Results would determine landfill classification, i .e. , I, II, III or unclas- <br /> sified, which in turn will dictate closure requirements or any additional <br /> work necessary. <br /> Additionally, J-M landfills have been placed in Rank 4 of Calderon's Solid <br /> Waste Assessment List. Rank 4 facilities must submit their SWAT by April 1989 <br /> and complete their SWAT report by July 1990. To avoid any future work, I <br /> suggested the current ground water monitoring system be designed in accordance <br /> with Calderon requirements. J-M officials were receptive to this suggestion. <br /> 2. Ponds <br /> Two ponds on-site receive process and cooling water. Water samples from <br /> 19861 indicated all constituents are well below drinking water standards <br /> with the exception of mercury and chromium. Aqueous concentrations of mercury <br /> and total chromium in the pond ranged from 2-3 ppb and 95-145 ppb, respec- <br /> tively. Drinking water standards are 2 ppb for mercury and 50 ppb for total <br /> chromium. Considering expected attenuations in the soil column and aquifer <br /> dilution, existing mercury concentrations are not an obvious problem. <br /> Unfortunately, no information is available prior to 1986 to assess if 1986 <br /> concentrations are representative. Ground water monitoring wells may be, <br /> warranted. <br /> J/M officials inquired about the possibility of leaving pond sludge in place <br /> and closing the pond 's in-situ. As previously discussed, the sludge has no <br /> priority pollutants or appreciable metal content. The only concern would be <br /> TDS and mineral leachability. Analysis using WET methodology (Title 22, <br /> California Administrative, Section 66700) specifying deionized water would <br /> answer this question. <br /> However, 1986 inspections of the ponds indicated that achieving a minimum 2' <br /> cover needed for in-situ pond closure may be difficult. Staff recommended that <br /> sludge be disposed of in on-site landfills, if appropriate. On-site landfill <br /> disposal is contingent upon landfill ground water monitoring and analysis of <br /> pond sludge. <br /> 3. Soils <br /> During inspections, crushed pipe and numerous gray-white deposits were noted <br /> surrounding the ponds and on dirt access roads. Kleinfelder's boring logs <br /> noted asbestos in the upper 1 '-6' depending on location. This material may be <br /> carried to Little John Creek by storm runoff. Since asbestos has been placed <br /> on the Proposition 65 list, no discharge of asbestos materials to surface <br /> waters will be allowed after November 1988. <br /> 1(J/M A-C Pipe Corporation "Report of Disposal Site Information° J. H. Klein- <br /> felder and Assoc. 1986) <br />