ANS is committed to advancing, fostering, and promoting the development and application of nuclear sciences and technologies to benefit society.
Explore the many uses for nuclear science and its impact on energy, the environment, healthcare, food, and more.
Explore membership for yourself or for your organization.
Conference Spotlight
2026 ANS Annual Conference
May 31–June 3, 2026
Denver, CO|Sheraton Denver
Latest Magazine Issues
Apr 2026
Jan 2026
Latest Journal Issues
Nuclear Science and Engineering
May 2026
Nuclear Technology
March 2026
Fusion Science and Technology
Latest News
DOE consortium begins new initiative aimed at growing fuel cycle
The U.S Department of Energy’s Office of Nuclear Energy, through its Defense Production Act (DPA) Nuclear Fuel Cycle Consortium, has begun a new initiative aimed at securing the nation’s nuclear fuel supply chain.
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.