12 research outputs found
Method for Ultratrace Level <sup>241</sup>Am Determination in Large Soil Samples by Sector Field-Inductively Coupled Plasma Mass Spectrometry: With Emphasis on the Removal of Spectral Interferences and Matrix Effect
A new method using
sector field-inductively coupled plasma mass
spectrometry (SF-ICPMS) was developed for the determination of <sup>241</sup>Am in large soil samples to provide realistic soil-plant
transfer parameter data for dose assessment of nuclear waste disposal
plans. We investigated four subjects: extraction behaviors of interfering
elements (Bi, Tl, Hg, Pb, Hf, and Pt) on DGA resin (normal type, abbreviated
as DGA-N); soil matrix element removal (Mg, Fe, Al, K, Na) using FeÂ(OH)<sub>3</sub>, CaF<sub>2</sub>, and CaC<sub>2</sub>O<sub>4</sub> coprecipitations;
Am and rare earth elements (REEs) separation on DGA-N and TEVA resins;
and optimization of SF-ICPMS (equipped with a high efficiency nebulizer
(HEN)) for Am determination. Our method utilized concentrated HNO<sub>3</sub> to leach Am from 2 to 20 g soil samples. The CaC<sub>2</sub>O<sub>4</sub> coprecipitation was used to remove major metals in
soil and followed by Am/interfering elements separation using the
proposed UTEVA + DGA-N procedure. After a further separation of REEs
on TEVA resin, <sup>241</sup>Am was determined by HEN-SF-ICPMS. This
method eliminated the matrix effect in ICPMS <sup>241</sup>Am measurement
for large soil samples. The high decontamination factors (DFs) of
interfering elements enable their thorough removal, and in particular,
the DF of Pu (7 × 10<sup>5</sup>) was the highest ever reported
in <sup>241</sup>Am studies; thus, this method is capable of analyzing <sup>241</sup>Pu-contaminated Fukushima Daiichi Nuclear Power Plant (FDNPP)
sourced soil samples. A low detection limit of 0.012 mBq g<sup>–1</sup> for <sup>241</sup>Am was achieved. The chemical recovery of Am (76–82%)
was stable for soil samples. This method can be employed for the low
level <sup>241</sup>Am determination in large size soil samples that
are contaminated with <sup>241</sup>Pu
High-Performance Method for Determination of Pu Isotopes in Soil and Sediment Samples by Sector Field-Inductively Coupled Plasma Mass Spectrometry
Plutonium is extensively
studied in radioecology (e.g., soil to
plant transfer and radiological assessment) and geochemistry (e.g.,
sediment dating). Here, we reported a new chemical separation method
for rapid determination of Pu in soil and sediment samples, based
on the following investigations: extraction behaviors of interfering
elements (IEs, for inductively coupled plasma mass spectrometry (ICPMS)
measurement) on TEVA resin; decontamination of U using TEVA, UTEVA,
and DGA resins; and the impact of coprecipitation on Pu determination.
The developed method consists of four steps: HNO<sub>3</sub> leaching
for Pu release; CaF<sub>2</sub>/LaF<sub>3</sub> coprecipitation for
the removal of major metals and U; the proposed TEVA + UTEVA + DGA
procedure for the removal of U, Pb, Bi, Tl, Hg, Hf, Pt, and Dy; and
ICPMS measurement. The accuracy of this method in determining <sup>239+240</sup>Pu activity and <sup>240</sup>Pu/<sup>239</sup>Pu and <sup>241</sup>Pu/<sup>239</sup>Pu isotopic ratios was validated by analyzing
five standard reference materials (soil, fresh water sediment, and
ocean sediment). This method is characterized by its stable and high
Pu recovery (90–97% for soil; 92–98% for sediment) and
high decontamination factor of U (1.6 × 10<sup>7</sup>), which
is the highest reported for soil and sediment samples. In addition,
the short analytical time of 12 h and the method detection limits,
which are the lowest yet reported in literature, of 0.56 μBq
g<sup>–1</sup> (0.24 fg g<sup>–1</sup>) for <sup>239</sup>Pu, 1.2 μBq g<sup>–1</sup> (0.14 fg g<sup>–1</sup>) for <sup>240</sup>Pu, and 0.34 mBq g<sup>–1</sup> (0.09
fg g<sup>–1</sup>) for <sup>241</sup>Pu (calculated on the
basis of a 1 g soil sample) allow the rapid determination of ultratrace
level Pu in soil and sediment samples
Brain Radiotherapy plus Concurrent Temozolomide versus Radiotherapy Alone for Patients with Brain Metastases: A Meta-Analysis
<div><p>Objective</p><p>We performed a meta-analysis of randomized clinical trials to compare the efficacy of brain radiotherapy (RT) combined with temozolomide (TMZ) versus RT alone as first-line treatment for brain metastases (BM).</p><p>Methods</p><p>Medline, Embase, and Pubmed were used to search for relevant randomized controlled trials (RCTs). Two investigators reviewed the abstracts and independently rated the quality of trials and relevant data. The primary outcome was overall survival (OS). Secondary outcomes included progression-free survival (PFS), objective response rate (ORR), and adverse events.</p><p>Results</p><p>Seven studies were selected from the literature search. RT plus TMZ produced significant improvement in ORR with odds ratio (OR) of 2.27 (95% CI, 1.29 to 4.00; <i>P</i> = 0.005) compared with RT alone. OS and PFS were not significantly different between the two arms (OS: HR, 1.00; <i>P</i> = 0.959; PFS: HR, 0.73; <i>P</i> = 0.232). However, the RT plus TMZ arm was associated with significantly more grade 3 to 4 nausea and thrombocytopenia.</p><p>Conclusion</p><p>Concomitant RT and TMZ, compared to RT alone, significantly increases ORR in patients with BM, but yields increased toxicity and fails to demonstrate a survival advantage.</p></div
Forest plot of severe toxicities: (A) nausea; (B) thrombocytopenia.
<p>*Favors RT+TMZ = Lower risk in RT+TMZ.</p
Hazard ratios (HR) and 95% CIs for progression-free survival (PFS).
<p>Hazard ratios (HR) and 95% CIs for progression-free survival (PFS).</p
Forest plot of overall survival (OS) for patients with brain metastases (BM).
<p>Forest plot of overall survival (OS) for patients with brain metastases (BM).</p
Forest plot of subgroup analysis by cancer type for OS.
<p>Forest plot of subgroup analysis by cancer type for OS.</p
A flow chart showing the progress of trials through the review.
<p>A flow chart showing the progress of trials through the review.</p