1968 to at least 1989 the Atomic Energy Commission numbers for GRHS were 29-12957-01 and 29-12957-02 Update below, it was removed in 1991.
I grew up in this town in New Jersey, 11 miles due west of the Empire State Building where the EPA found Uranium, Thorium and Radium under our Little League Field at Carteret Park, and the next town over was Bloomfield New Jersey that had the Westinghouse Uranium and Thorium processing plant. But I just found that we had a device, the Gammaton 50B which contained 400 curies of Cesium 137 and was rated for 50,000 REM of radiation inside the chamber.
I will be posting the NRC correspondence and reports and you can decide for yourselves who is responsible. The man in charge was a good friend but he was way over his head on this and this whole mess is the result of the most destructive force known to man, the irresponsible Atomic Energy Commission that sent devices like this all over the country and the world on the “Atoms for Peace” initiative and they were also responsible for the atomic tests.
These documents are on the Nuclear Regulatory Commission Website and I will post the Title of document with link and then the screen shots of the pages
Google currently occupies the location where American Standard built portable nuclear reactors that were sent overseas in trade shows for the Atomic Energy Commission and for colleges and universities. The AEC shut down the facility because it was located in a densely populated area and given the accidents from these reactors and that the location had no shielding or even containment for the radioactive gasses and radioactive water, it was decided to pull the plug on the reactors. They had two reactors on site and built these reactors for other entities:
Iowa State University Virginia Polytechnic Institute / North Carolina State college Australia (Atomic Energy Commission) Japan (Kinki University) Osaka Japan (Tokai University)
From the report page 6:
“B. Reactor Building The reactor will be housed in an existing 20′ x 32′ x 14′ eave height steel frame reactor building. The building is supported on a reinforced concrete foundation and has corrugated steel walls and roof and a concrete floor sealed with Amercoat. A concrete curb around the base of the building will prevent run off of radioactive water. Gas-tight construction has not been provided. Entry to the building is provided by two sliding doors, which may be locked with a padlock. A stairway provides access to the top of the reactor. A one-ton electric hoist is available for removing the concrete closures from the reactor”
Note the curb around the building to prevent run off of radioactive water and the padlock on the door for security. Remember this is for two nuclear reactors.
This reactor type was based on the Argonne reactor which had some serious defects causing a melt down.
EXPERIMENTAL EVALUATION OF THE FALLOUT-RADIATION PROTECTION PROVIDED BY SELECTED STRUCTURES IN THE LOS ANGELES AREA February 26, 1963
“An experimental study designed to provide a basis for estimating protection against fallout radiation was conducted on four diversified structures in the Los Angeles, Calif., area. This study was sponsored by the Civil Effects Test Operations (CETO), Division of Biology and Medicine, U. S. Atomic Energy Commission. The four buildings studied were (1) the Laboratory of Nuclear Medicine and Radiation Biology at the University of California at Los Angeles (UCLA); (2) a family fallout shelter; (3) the communications section of the Los Angeles Police Department building; and (4) a typical classroom located at North Hollywood High School.
A fallout radiation field was simulated by the Mobile Radiological Measuring Unit. The unit employed a single radioactive Co 60 source, which was pumped at a uniform speed through a long length of tubing evenly distributed over the area of interest. Measurements of the radiation levels at selected points inside the structures were made with highly sensitive ionization chamber detectors. Protection factors ranged from 10 to 2000 in the UCLA building, up to 10,000 in the family fallout shelter, from 50 to 150 in the communications section of the police building, and from less than 10 to approximately 20 in the high school classroom.”
“The Site covers approximately 0.9 acre and was used for an orchard and flower growing business. Sequoia Union High School District (SUHSD) purchased the Site and planned for construction of a school facility for a charter school. The construction consisted of classrooms, a gymnasium and paved parking areas. The school campus is an expansion of the adjacent campus at 1010, 1020, 1040 and 1056 Myrtle Street (Site Code 204238) that was cleaned up under DTSC’s oversight in early 2011. In September 2013, SUHSD entered into a voluntary cleanup agreement with DTSC for cleanup of the soil contamination. The Site was cleaned up by soil excavation, capping and offsite disposal. Soil contaminated with arsenic, lead, dieldrin and DDT was excavated from classroom building locations and consolidated in a 0.5-acre area onsite that will be used for parking and gymnasium. Approximately 305 cubic yards of excess contaminated soil that cannot be used onsite was disposed of to a permitted landfill. The Site cleanup and school construction was completed in September 2014.” Continue reading “East Palo Alto – MYRTLE STREET HIGH SCHOOL CAMPUS PHASE 2 (60001925)”→
Map of the site is on page “The 22-acre site located at 400 Carolan Avenue, in Burlingame. It is the existing Burlingame High School (built in the late 1910s). DTSC reviewed a Phase I Environmental Site Assessment (Phase I) and determined that a Preliminary Environmental Assessment (PEA) was required.
A Preliminary Environmental Assessment (PEA, 2003/04) investigated the site for metals, organochlorine pesticides, polychlorinated biphenyl (PCB), total petroleum hydrocarbons, volatile organic compounds and metals. The PEA report identified lead and PCB around the main building, and elevated arsenic in the athletic field. DTSC issued further action for Lead/PCB, and additional investigation for the arsenic.
Supplemental site investigations defined the extent of lead impacted soils and identified elevated levels of arsenic in soils in various areas of the campus. A Removal Action Workplan (RAW) for lead and PCBs was approved for implementation in December 2005 for areas around the main building. The removal began in January 2006 and was completed in June 2007. Financial hardship caused delays in the completion of the removal. Once financial issues were resolved, the District took confirmation samples to confirm clean-up goals were met. Continue reading “BURLINGAME HIGH SCHOOL (41820008) on toxic waste site”→