Centre for Radiochemistry Research, School of Chemistry, University of Manchester, M13 9PL, UK.
Environ Sci Process Impacts. 2018 Jun 20;20(6):956-964. doi: 10.1039/c8em00073e.
One of the nuclear fuel storage ponds at Sellafield (United Kingdom) is open to the air, and has contained a significant inventory of corroded magnox fuel and sludge for several decades. As a result, some fission products have also been released into solution. 90Sr is known to constitute a small mass of the radionuclides present in the pond, but due to its solubility and activity, it is at risk of challenging effluent discharge limits. The sludge is predominantly composed of brucite (Mg(OH)2), and organic molecules are known to be present in the pond liquor with occasional algal blooms restricting visibility. Understanding the chemical interactions of these components is important to inform ongoing sludge retrievals and effluent management. Additionally, interactions of radionuclides with organics at high pH will be an important consideration for the evolution of cementitious backfilled disposal sites in the UK. Batch sorption-desorption experiments were performed with brucite, 90Sr and natural organic matter (NOM) (humic acid (HA) and Pseudanabaena catenata cyanobacterial growth supernatant) in both binary and ternary systems at high pH. Ionic strength, pH and order of addition of components were varied. 90Sr was shown not to interact strongly with the bulk brucite surface in binary systems under pH conditions relevant to the pond. HA in both binary and ternary systems demonstrated a strong affinity for the brucite surface. Ternary systems containing HA demonstrated enhanced sorption of 90Sr at pH 11.5 and vice versa, likely via formation of strontium-humate complexes regardless of the order of addition of components. The distribution coefficients show HA sorption to be reversible at all pH values studied, and it appeared to control 90Sr behaviour at pH 11.5. Ternary systems containing cyanobacterial supernatant demonstrated a difference in 90Sr behaviour when the culture had been subjected to irradiation in the first stages of its growth.
塞拉菲尔德(英国)的一个核燃料储存池是露天的,几十年来一直存放着大量腐蚀的镁诺克斯燃料和污泥。因此,一些裂变产物也已释放到溶液中。已知 90Sr 构成了池中的放射性核素的一小部分质量,但由于其可溶性和活性,它有挑战废水排放限制的风险。污泥主要由水镁石(Mg(OH)2)组成,已知池液中存在有机分子,偶尔藻类大量繁殖会限制能见度。了解这些成分的化学相互作用对于正在进行的污泥回收和废水管理非常重要。此外,高 pH 值下放射性核素与有机物的相互作用将是英国水泥回填处置场演变的一个重要考虑因素。在高 pH 值下,在二元和三元体系中进行了水镁石、90Sr 和天然有机物(NOM)(腐殖酸(HA)和 Pseudanabaena catenata 蓝藻生长上清液)的批量吸附-解吸实验。改变离子强度、pH 值和组分的添加顺序。在与池塘相关的 pH 条件下,在二元体系中,90Sr 未与大块水镁石表面强烈相互作用。HA 在二元和三元体系中均表现出对水镁石表面的强烈亲和力。在 pH 11.5 时,含 HA 的三元体系表现出对 90Sr 的增强吸附,反之亦然,可能是形成了锶-腐殖酸盐复合物,而不管添加组件的顺序如何。分配系数表明,在所有研究的 pH 值下,HA 吸附都是可逆的,并且在 pH 11.5 时似乎控制着 90Sr 的行为。当培养物在其生长的早期阶段受到辐照时,含蓝藻上清液的三元体系表现出 90Sr 行为的差异。