Details
Original language | English |
---|---|
Pages (from-to) | 1765-1769 |
Number of pages | 5 |
Journal | Journal of Radioanalytical and Nuclear Chemistry |
Volume | 307 |
Issue number | 3 |
Early online date | 14 Aug 2015 |
Publication status | Published - 1 Mar 2016 |
Abstract
Processing environmental samples for analysis can result in loss of target or bystander radionuclides. Removal of carrier-free 131I from soil samples by chemical processes was evaluated in the presence and absence of iodide carrier, H2O2, and AgNO3. Soil samples spiked with 131I and 134Cs tracer were boiled under reflux for 30 min in HNO3 and combinations of aforementioned reagents. Spectroscopic analysis revealed the greatest removal of radioiodine (45 ± 1 %) was achieved using AgNO3 and carrier; the lowest (7 ± 1 %) was achieved by refluxing with H2O2 and HNO3. The results quantify the effect of iodide carrier and suggest the preferential interaction of H2O2 with iodide instead of soil organic matter.
Keywords
- Carrier effect, Decontamination, Hydrogen peroxide, Radioiodine, Soil, Soil organic matter
ASJC Scopus subject areas
- Chemistry(all)
- Analytical Chemistry
- Energy(all)
- Nuclear Energy and Engineering
- Medicine(all)
- Radiology Nuclear Medicine and imaging
- Environmental Science(all)
- Pollution
- Chemistry(all)
- Spectroscopy
- Medicine(all)
- Public Health, Environmental and Occupational Health
- Environmental Science(all)
- Health, Toxicology and Mutagenesis
Sustainable Development Goals
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In: Journal of Radioanalytical and Nuclear Chemistry, Vol. 307, No. 3, 01.03.2016, p. 1765-1769.
Research output: Contribution to journal › Article › Research › peer review
}
TY - JOUR
T1 - Preparedness for a nuclear accident
T2 - removal of radioiodine from soil by chemical processing
AU - Rosenberg, Brett L.
AU - Steinhauser, Georg
N1 - This work was supported by CDC NIOSH Mountain and Plains Education and Research Center (Grant Number T42OH009229-07) and the US Nuclear Regulatory Commission (NRC) (Grant Number NRC-HQ-12-G-38-0044). Its contents are solely the responsibility of the authors and do not necessarily represent the official view of the CDC NIOSH and MAP ERC.
PY - 2016/3/1
Y1 - 2016/3/1
N2 - Processing environmental samples for analysis can result in loss of target or bystander radionuclides. Removal of carrier-free 131I from soil samples by chemical processes was evaluated in the presence and absence of iodide carrier, H2O2, and AgNO3. Soil samples spiked with 131I and 134Cs tracer were boiled under reflux for 30 min in HNO3 and combinations of aforementioned reagents. Spectroscopic analysis revealed the greatest removal of radioiodine (45 ± 1 %) was achieved using AgNO3 and carrier; the lowest (7 ± 1 %) was achieved by refluxing with H2O2 and HNO3. The results quantify the effect of iodide carrier and suggest the preferential interaction of H2O2 with iodide instead of soil organic matter.
AB - Processing environmental samples for analysis can result in loss of target or bystander radionuclides. Removal of carrier-free 131I from soil samples by chemical processes was evaluated in the presence and absence of iodide carrier, H2O2, and AgNO3. Soil samples spiked with 131I and 134Cs tracer were boiled under reflux for 30 min in HNO3 and combinations of aforementioned reagents. Spectroscopic analysis revealed the greatest removal of radioiodine (45 ± 1 %) was achieved using AgNO3 and carrier; the lowest (7 ± 1 %) was achieved by refluxing with H2O2 and HNO3. The results quantify the effect of iodide carrier and suggest the preferential interaction of H2O2 with iodide instead of soil organic matter.
KW - Carrier effect
KW - Decontamination
KW - Hydrogen peroxide
KW - Radioiodine
KW - Soil
KW - Soil organic matter
UR - http://www.scopus.com/inward/record.url?scp=84939238635&partnerID=8YFLogxK
U2 - 10.1007/s10967-015-4376-y
DO - 10.1007/s10967-015-4376-y
M3 - Article
AN - SCOPUS:84939238635
VL - 307
SP - 1765
EP - 1769
JO - Journal of Radioanalytical and Nuclear Chemistry
JF - Journal of Radioanalytical and Nuclear Chemistry
SN - 0236-5731
IS - 3
ER -