Ravensburg-Weingarten University, Doggenriedstr., D-88250, Weingarten, Germany.
Ravensburg-Weingarten University, Doggenriedstr., D-88250, Weingarten, Germany.
J Environ Radioact. 2021 Jun;232:106584. doi: 10.1016/j.jenvrad.2021.106584. Epub 2021 Mar 18.
The Aare-Rhine river system with its four nuclear power plants on the banks of these rivers and with its intermediate lakes and reservoirs provide the unique chance to analyze the input of radioactivity into the system thereby furnishing information on the sources, to analyze the transport within the sediment and along the rivers, and to refine unsupported Pb dating validated by known discharge maxima. At three locations (Lake Biel, Klingnau Reservoir, old branch of the Rhine) in the Aare and Rhine rivers system downstream of the older nuclear power plants (NPPs) Mühleberg and Beznau, the vertical distributions of Cs, Pb, Pb, Bi, K, Be, Pu, Pu, Am, and Np in sediment cores were determined. Depth-age relations using the excess 210 Pb were established with the raw and with the piecewise Constant Rate Supply (CRS) models. A comparison of the piecewise CRS method with the imprints of known discharges showed differences of up to two years. Besides typical Cs signals (about 100 Bq∙kg) from the atmospheric nuclear weapons testing (NWT) and the Chernobyl fallouts, imprints of known Cs discharges (10-70 Bq∙kg) from the NPPs were found in the sediments. The Np distributions (6-10 Bq∙kg) essentially follow the Cs NWT distributions. In the sediment downstream the NPP Mühleberg (Lake Biel) aPu distribution (<3 Bq∙kg) was found, which was solely due to the NWT fallout. Downstream the NPP Beznau (Klingnau Reservoir and an old branch of the Rhine), besides the NWT distribution, also imprints of Pu discharges (up to 7 Bq∙kg) were found within the time interval 1963 to 1986.Pu/Pu ratios revealed that the burn-up times of the nuclear fuel in the NPP (U enrichment of 3.5%), from which the discharges stem, should be about 1 year or less. A comparison between the calculated and the measured Cs/Pu ratio revealed no large discrepancies for the Lake Biel and Rhine positions, but in the Klingnau distribution, the calculated Cs/Pu ratio is one order of magnitude larger than the measured one. The reason could be either a natural uranium research reactor as the source, or strong, short-range Pu precipitation after the discharge from the Beznau NPP. The largest Pu peak in the Rhine sediment (1968/70) corresponds to no major peak in the Klingnau sediment. For the NPP Mühleberg discharge of 1982 the ratio of the Cs deposition in sediments from Lake Biel, Klingnau Reservoir and the Rhine river is about 1 : 0.5 : 2.9. For the 1977/78 Pu deposition the ratio is 1 : 0.02, for the Klingnau Reservoir and the Rhine sediments, respectively. These numbers indicate a long-range transport of Cs and a rather short-range transport of Pu.
阿尔河-莱茵河系统及其四条位于这些河流两岸的核电站,以及其中间湖泊和水库,为分析放射性物质进入系统的情况提供了独特的机会,从而提供了有关来源的信息,分析了沉积物和河流内部的输运情况,并改进了经已知流量最大值验证的未支持的 Pb 测年。在阿尔河和莱茵河系统的三个地点(下旧核电站(NPP)Mühleberg 和 Beznau 下游的比耶尔湖、克林瑙水库和莱茵河旧支流),测定了沉积物岩芯中 Cs、Pb、Bi、K、Be、Pu、Am 和 Np 的垂直分布。使用过剩的 210Pb 建立了年龄-深度关系,使用原始模型和分段恒定供应率(CRS)模型。分段 CRS 方法与已知排放物的印记进行比较,发现存在长达两年的差异。除了来自大气核武器试验(NWT)和切尔诺贝利沉降物的典型 Cs 信号(约 100 Bq·kg)外,还在沉积物中发现了来自 NPP 的已知 Cs 排放物(10-70 Bq·kg)的印记。Np 分布(6-10 Bq·kg)基本遵循 Cs NWT 分布。在 NPP Mühleberg(比耶尔湖)下游,发现了<3 Bq·kg 的 aPu 分布,这完全是由于 NWT 沉降物造成的。在 NPP Beznau(克林瑙水库和莱茵河旧支流)下游,除了 NWT 分布外,还在 1963 年至 1986 年的时间间隔内发现了 Pu 排放量(高达 7 Bq·kg)的印记。Pu/Pu 比值表明,NPP(U 富集度为 3.5%)中核燃料的燃烧时间应约为 1 年或更短。计算的 Cs/Pu 比值与实测值之间的比较表明,比耶尔湖和莱茵河位置没有大的差异,但在克林瑙分布中,计算的 Cs/Pu 比值比实测值大一个数量级。原因可能是天然铀研究反应堆作为源,或者是贝兹瑙 NPP 排放后 Pu 的强烈、短程沉淀。莱茵河沉积物中最大的 Pu 峰值(1968/70 年)与克林瑙沉积物中没有明显的峰值相对应。对于 1982 年 Mühleberg NPP 的排放量,比耶尔湖、克林瑙水库和莱茵河沉积物中 Cs 沉积的比例约为 1:0.5:2.9。对于 1977/78 年 Pu 的沉积,比例分别为 1:0.02 和克林瑙水库和莱茵河沉积物。这些数字表明 Cs 的长程输运和 Pu 的短程输运。