Laserfiche WebLink
A <br /> NATE OF CALIFORNIA—HEALTH AND WELFARE CY EDMUND G. BROWN JR.,Governor <br /> DEPARTMENT OF HEALTH SERVICES <br /> 714/744 P STREET <br /> SACRAMENTO, CA 45814 <br /> (9 16) 324-1807 r=y3 <br /> July 19, 1982 <br /> JAL r <br /> Mr. James N. Siegfried, Manage r j d:A l 1 D',S r LCT <br /> Community Environmental Standards <br /> Manville Service Corporation <br /> Ken-Caryl Ranch <br /> Denver, CO 80217 <br /> Dear Mr. Siegfried: <br /> This is in response to your letter of March 29, 19$2 and the enclosed report <br /> describing your asbestos-cement pipe- rejects and process wastes (M-03) generated <br /> at your Stockton, California plant. These submitted materials constitute an <br /> application for a nonhazardous classification pursuant to Section 66305, Chapter <br /> 30, Division 4, Title 22, California Administrative Code. <br /> Asbestos-cement pipe is manufactured using a wet process. A pumpable slurry is <br /> formed by blending portland cement (50%) with sand and silica flour (35%) and <br /> asbestos fiber (15%) in aqueous suspension. These ingredients are formed into <br /> a thin wet sheet by filtration and wrapped onto the circumference of a rotating <br /> round steel core. The pipe is cured first by air followed by steam in an auto- <br /> clave unit. <br /> The wastes can be categorized as follows: <br /> I . Product rejects - fully cured pipe, pieces, and couplings. The character <br /> of these wastes does not differ from actual finished product. <br /> 2. Process rejects - nonfriable machine cleanings and pipe rejected prior to <br /> autoclaving. Except for shape these kinds of wastes would be very similar <br /> to finished product. <br /> 3. Wrapping wastes - bags that contained imported asbestos and are likely to <br /> retain a light layer of fiber dust on the inner lining. The bags are folded <br /> and housed in a plastic wrapper which is then heat-shrunk to encapsulate re- <br /> sidual fibers. <br /> 4. Basin sediments - inert process ingredients which pass through the filtration <br /> septum and the wastewater system. These materials , which are ultimately de- <br /> posited as sediments in settling basins, are relatively high in reactive cement <br /> and low in fiber content due to preferential interception at the point of <br /> filtration. <br /> Waste types 1 , 2, and 3 above are not considered hazardous asbestos wastes because <br /> they are nonfriable and contain no significant amount of free particulate asbestos <br /> fiber. As such, they do not possess the potential of producing airborne, respir- <br /> able asbestos fibers. The department considers an asbestos waste to be hazardous <br /> only if this potential exists due to friability or particulate form. <br />