首页> 外文期刊>Journal of Environmental Radioactivity >Effective half-lives of Cs-137 in giant butterbur and field horsetail, and the distribution differences of potassium and Cs-137 in aboveground tissue parts
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Effective half-lives of Cs-137 in giant butterbur and field horsetail, and the distribution differences of potassium and Cs-137 in aboveground tissue parts

机译:Cs-137在巨大的款冬和野马尾中的有效半衰期,以及钾和Cs-137在地上组织部分中的分布差异

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Concentrations of Cs-137 and K-40 in different tissues of edible wild herbaceous plants, that is, leaf blade and petiole for giant butterbur (Petasites japonicas (Siebold et Zucc.) Maxim.), and leaf, stem and strobilus for fertile shoot of field horsetail(Equisetum arvense L) were measured in 2012-2014 to clarify the effect in Japan from the Fukushima Daiichi Nuclear Power Plant accident. The concentrations of Cs-137 decreased with time with effective half-lives of ca. 450 d and 360 d for giant butterbur and field horsetail, respectively. The ANOVA test revealed that K-40 and Cs-137 distributions in leaf blade and petiole for giant butterbur and leaf and stem for field horsetail were different. Therefore, other plants, leaf and stem for Japanese knotweed (Fallopia japonica (Houtt.) Ronse Decr.) and Canada goldenrod (Solidago canadensis L), and leaf blade and petiole for gingko (Ginkgo biloba L) and Someiyoshino cherry (Cerasus x yedoensis (Matsum.) A.V.Vassil. 'Somei-yoshino') were collected from the same sampling field and their Cs-137 and K-40 concentrations were compared to those in the giant butterbur and field horsetail parts. For Cs-137, concentrations in leaf blade and leaf parts were 1.1-6.0 times higher than those in petiole and stem parts for all six plants. On the other hand, K-40 concentrations in leaf blade and leaf parts were 0.40-0.97 of those observed in petiole and stem parts. Discrimination ratios of K-40/Cs-137 of leaf blade to petiole or leaf to stem were then calculated and they ranged from 0.09 to 0.57. These results suggested that Cs and K did not behave similarly in these plants. Thus, to understand the radiocesium fate in plants, K measurement results should not be used as an analog for Cs behavior although Cs is known to have a similar chemical reactivity to that of K. (C) 2015 Elsevier Ltd. All rights reserved.
机译:食用野生草植物的不同组织中Cs-137和K-40的浓度,即巨型金毛菜(Petasites japonicas(Siebold et Zucc。)Maxim。)的叶片和叶柄,以及可育芽的叶,茎和球茎的浓度。在2012年至2014年对田间马尾(木贼马)进行了测量,以阐明福岛第一核电站事故对日本的影响。 Cs-137的浓度随时间降低,有效半衰期为。巨大的款冬和野马尾分别为450 d和360 d。方差分析测试表明,大毛butter的叶片和叶柄的K-40和Cs-137分布以及田间马尾的叶片和茎的K-40和Cs-137分布不同。因此,日本虎杖(Fallopia japonica(Houtt。)Ronse Decr。)和加拿大菊科(Solidago canadensis L)的其他植物,叶和茎,以及银杏(Ginkgo biloba L)和Someiyoshino樱桃(Cerasus x yedoensis)的叶片和叶柄。 (Matsum。)AVVassil。'Somei-yoshino')是从相同的采样场中收集的,并将它们的Cs-137和K-40浓度与巨大的款冬和马尾部分的Cs-137和K-40浓度进行了比较。对于Cs-137,对于所有六种植物,叶片和叶片部分中的浓度均比叶柄和茎部中的浓度高1.1-6.0倍。另一方面,叶片和叶片部分中的K-40浓度为叶柄和茎部中观察到的K-40浓度为0.40-0.97。然后计算出叶片对叶柄或叶片对茎的K-40 / Cs-137的鉴别率,范围为0.09至0.57。这些结果表明,Cs和K在这些植物中的行为不同。因此,要了解植物中放射性铯的命运,尽管已知Cs的化学反应性与K相似,但不应将K的测量结果用作Cs行为的类似物。(C)2015 Elsevier Ltd.保留所有权利。

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