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NRC looks to leverage previous approvals for large LWRs
During this time of resurging interest in nuclear power, many conversations have centered on one fundamental problem: Electricity is needed now, but nuclear projects (in recent decades) have taken many years to get permitted and built.
In the past few years, a bevy of new strategies have been pursued to fix this problem. Workforce programs that seek to laterally transition skilled people from other industries, plans to reuse the transmission infrastructure at shuttered coal sites, efforts to restart plants like Palisades or Duane Arnold, new reactor designs that build on the legacy of research done in the early days of atomic power—all of these plans share a common throughline: leveraging work already done instead of starting over from square one to get new plants designed and built.
Byung-Soo Lee, William A. Jester
Nuclear Technology | Volume 114 | Number 1 | April 1996 | Pages 122-134
Technical Paper | Material | doi.org/10.13182/NT96-A35228
Articles are hosted by Taylor and Francis Online.
Mechanisms of radioiodine deposition from sample air containing both gaseous and particulate radioiodine in reactor sample lines are studied, and experimental methods are developed. A short half-lived radioiodine tracer, 128I (t1/2 = 25 min), is used in the chemical forms of molecular iodine and methyl iodide. An effort is made to investigate the type of particles for particulate iodine. Of the various types of particles tested, only tobacco smoke particles have a sufficiently high iodination rate to be used in these studies. The 609.6-cm (20-ft)-long sample lines of Types 316 and 304 stainless steel tube (2.29 cm i.d.) were tested for the sample flow rates of 28.3 ℓ/min (1 ft3/min) and 56.6 ℓ/min (2 ft3/min). In-tube measurements using a calibrated thin-walled Geiger tube are conducted to determine the penetration factor and space-dependent deposition velocity profile of radioiodine. Methyl iodide is not reactive for either the tube surfaces or aerosol particles. The overall deposition velocity of the mixture of the smoke particles and molecular iodine is higher than that of molecular iodine alone for similar sampling conditions. It is concluded that the high deposition rate of radioiodine in the sample air mixed with smoke particles and molecular iodine is caused by the different sample line surfaces that are contaminated with smoke particles.