<p>A sensitivity study was performed on method-blank samples for alpha spectrometry. The samples of water, analyzed for <sup>239</sup>Pu and U-nat (<sup>234</sup>U, <sup>235</sup>U, <sup>238</sup>U) isotopes, were spiked with the <sup>236</sup>Pu and <sup>232</sup>U isotope-dilution tracers. The effects of various methods of uncertainty propagation and corrections were studied. In addition, classical detection limits were calculated in terms of decision level, detection limit, upper limit, and determination limit. Cases of zero counts were compared with the Bayesian theory of zero-count detector. Also, detection limits according to the Safe Drinking Water Act definition were calculated. Using the proposed continuity correction, a 4.7% of false-positive rates was observed. The average minimum detectable activities calculated were 0.61, 0.81, 0.82, and 0.74&#xa0;mBq L<sup>−1</sup> for <sup>239</sup>Pu, <sup>234</sup>U, <sup>235</sup>U, and <sup>238</sup>U, respectively.</p>

错误:搜索内容不能为空,请输入英文关键词
错误:关键词超出字数限制,请精简
高级检索

Detection capability of environmental alpha spectrometry: II. Sensitivity

  • Thomas M. Semkow,
  • Adam G. Burn

摘要

A sensitivity study was performed on method-blank samples for alpha spectrometry. The samples of water, analyzed for 239Pu and U-nat (234U, 235U, 238U) isotopes, were spiked with the 236Pu and 232U isotope-dilution tracers. The effects of various methods of uncertainty propagation and corrections were studied. In addition, classical detection limits were calculated in terms of decision level, detection limit, upper limit, and determination limit. Cases of zero counts were compared with the Bayesian theory of zero-count detector. Also, detection limits according to the Safe Drinking Water Act definition were calculated. Using the proposed continuity correction, a 4.7% of false-positive rates was observed. The average minimum detectable activities calculated were 0.61, 0.81, 0.82, and 0.74 mBq L−1 for 239Pu, 234U, 235U, and 238U, respectively.