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Colin Judge: Testing structural materials in Idaho’s newest hot cell facility
Idaho National Laboratory’s newest facility—the Sample Preparation Laboratory (SPL)—sits across the road from the Hot Fuel Examination Facility (HFEF), which started operating in 1975. SPL will host the first new hot cells at INL’s Materials and Fuels Complex (MFC) in 50 years, giving INL researchers and partners new flexibility to test the structural properties of irradiated materials fresh from the Advanced Test Reactor (ATR) or from a partner’s facility.
Materials meant to withstand extreme conditions in fission or fusion power plants must be tested under similar conditions and pushed past their breaking points so performance and limitations can be understood and improved. Once irradiated, materials samples can be cut down to size in SPL and packaged for testing in other facilities at INL or other national laboratories, commercial labs, or universities. But they can also be subjected to extreme thermal or corrosive conditions and mechanical testing right in SPL, explains Colin Judge, who, as INL’s division director for nuclear materials performance, oversees SPL and other facilities at the MFC.
SPL won’t go “hot” until January 2026, but Judge spoke with NN staff writer Susan Gallier about its capabilities as his team was moving instruments into the new facility.
Byung-Soo Lee, William A. Jester
Nuclear Technology | Volume 113 | Number 2 | February 1996 | Pages 221-231
Technical Paper | Reactor Operation | doi.org/10.13182/NT96-A35190
Articles are hosted by Taylor and Francis Online.
Experimental methods are developed, and the mechanisms of airborne radioiodine deposition in reactor sample lines are studied. A short-half-lived radioiodine tracer, 128I (t1/2 = 25 min), is used in the chemical forms of molecular iodine and methyl iodide. In-tube measurements using a calibrated Geiger tube are conducted to determine the space-dependent iodine deposition rate and the penetration factor. The reproducibility of average deposition velocity and thus penetration factors for a given sample line under similar experimental conditions show good improvement over those of previous researchers. For the three stainless steel tubes tested under comparable conditions, the deposition velocities are tube specific, with the difference in deposition velocities being a factor of >10. The most important factors that determine the I2 deposition rate are organic contamination, sample air relative humidity, and sample line inside surface structures. Heat tracing and passivation procedures are found to be effective in reducing I2 deposition rate. The CdI2 filter in the iodine sampler system showed a retention efficiency of ∼81% under the test conditions rather than the 98% reported by the manufacturer. In conclusion, in-plant testing is necessary to determine the deposition losses of airborne radioiodine in the existing plant sample lines. The sample lines should be cleaned at regular intervals and heat traced to minimize the deposition losses. For very long sample lines, passivation procedures may be required.