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沉积在城市表面的134Cs和85Sr气溶胶的解吸机制。

Mechanisms of desorption of 134Cs and 85Sr aerosols deposited on urban surfaces.

作者信息

Real J, Persin F, Camarasa-Claret C

机构信息

Department of Environmental Protection, Institute of Protection and Nuclear Safety, Saint-Paul-Lez-Durance, France.

出版信息

J Environ Radioact. 2002;62(1):1-15. doi: 10.1016/s0265-931x(01)00136-9.

Abstract

The radioactive isotopes of cesium and strontium may be deposited on urban surfaces in the case of an accidental atmospheric discharge from a nuclear facility and thus imply a health hazard. In order to handle the decontamination of these surfaces, we have carried out experiments under controlled conditions on tiles and concrete and we have studied.the physical and chemical mechanisms at the solid-liquid interface. The deposition of radionuclides was carried out in the form of aerosols indicating an accidental source term. Their desorption by rainwater is low in all cases, of the order of 5-6% for cesium for any material and 29 and 12% for strontium on tile and concrete, respectively. The low desorption values of cesium may be explained by the strong bonding that occurs with the silicates constituting the tile due to virtually irreversible processes of exchange of ions and by the formation of insoluble complexes with the C--S-H gel of concrete. The strontium-tile bonds are weaker, while strontium precipitates with the carbonates of concrete in the form of SrCO3. In view of these characteristics, washing solutions with high concentrations of chloride and oxalate of ammonium chosen for their ion-exchanging and sequestering properties were tested on these surfaces. The desorption of cesium improved strongly since it reached 70% on tile and 90% on concrete after 24h of contact, which is consistent with our knowledge of the; bonds between this element and the surfaces. Strontium, given the greater complexity of physical and chemical forms that it may take is less well desorbed. The ammonium chloride improves the desorption (50% and 40%, for tile and concrete, respectively) but the oxalate, while it does not affect desorption on the tiles, decreases that on the concrete since by strongly etching the concrete, it causes the release of carbonate ions that precipitate with strontium.

摘要

在核设施发生意外大气排放的情况下,铯和锶的放射性同位素可能会沉积在城市表面,从而构成健康危害。为了处理这些表面的去污问题,我们在可控条件下对瓷砖和混凝土进行了实验,并研究了固液界面的物理和化学机制。放射性核素以气溶胶形式沉积,表明存在意外源项。在所有情况下,它们被雨水的解吸率都很低,铯在任何材料上的解吸率约为5 - 6%,锶在瓷砖和混凝土上的解吸率分别为29%和12%。铯的低解吸值可以通过与构成瓷砖的硅酸盐发生的强键合来解释,这是由于离子交换的几乎不可逆过程以及与混凝土的C-S-H凝胶形成不溶性络合物。锶与瓷砖的键较弱,而锶与混凝土的碳酸盐以SrCO3的形式沉淀。鉴于这些特性,我们对这些表面测试了具有高浓度氯化铵和草酸铵的洗涤溶液,它们因其离子交换和螯合特性而被选用。铯的解吸率大幅提高,因为接触24小时后,它在瓷砖上的解吸率达到70%,在混凝土上达到90%,这与我们对该元素与表面之间键合的了解一致。由于锶可能具有更复杂的物理和化学形式,其解吸效果较差。氯化铵提高了解吸率(瓷砖和混凝土分别为50%和40%),但草酸铵虽然不影响瓷砖上的解吸,但会降低混凝土上的解吸率,因为它会强烈蚀刻混凝土,导致释放出与锶沉淀的碳酸根离子。

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