THE CHEMICAL AND MINERAL COMPOSITION OF NATURAL ZEOLITES AND THEIR SORPTION PROPERTIES DURING OZONATION WITH DRAIN WATER FROM NUCLEAR POWER PLANTS

IF 0.5 Q4 MINERALOGY Mineralogical Journal-Ukraine Pub Date : 2022-01-01 DOI:10.15407/mineraljournal.44.04.084
B. Shabalin, K. Yaroshenko, O. Lavrynenko, O. Pavlenko
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Abstract

The article reveals the regularities of the overall process of ozonolytic destruction of organic components of model drain water from nuclear power plants and sorption of imitators of the main dose-forming radionuclides (Cs — with the isotopic 137Cs label; stable isotopes of Co, Sr, Mn salts) by natural zeolite of the Sokyrnytsky deposit and sorption-reagent compounds — salts of ferrous and manganese (II). The chemical composition of the main elements of zeolite after ozonation with the addition of iron and manganese salts practically does not differ from the composition of natural zeolite. Its phase composition in the ozonation process in the presence of ferrum salts is represented by the main rock-forming mineral clinoptilolite and the secondary mineral — quartz. The main ferrum-containing phase on the zeolite surface is goethite. Secondary phases include Fe(II)-Fe(III) layered double hydroxides (Green Rust) and lepidocrocite, but their relative content is insignificant. For zeolites, after ozonation with the addition of both ferrous and manganese (II) salts, the main phases are clinoptilolite and quartz. Manganese-containing phases on the zeolite surface are represented by hausmannite Mn3O4, manganese (II) oxide, and manganese oxyhydroxide MnO(OH)2. The iron- and manganese-containing phases deposited on the surface of the zeolite in the process of ozonation are mainly characterized by a weakly crystallized or amorphized structure. The main sorbent of dose-forming radionuclides is zeolite, not the iron- and manganese-containing compounds that formed on its surface during ozonolysis. The maximum degree of sorption of 137Cs by zeolite is up to 90% when the concentration of Fe2+ is increased to 50 mg/dm3 or Mn2+ to 100 mg/dm3. The degree of cobalt sorption is 97.5% at the initial typical concentration of competing cations (Fe2+ — 5 mg/dm3; Mn2+ — 10 mg/dm3) and when Mn2+ concentration increases to 100 mg/dm3. The maximum degree of extraction of Sr2+ and Mn2+ is 99.4% and 99.9%, respectively. For effective extraction of 137Cs and Co2+ by zeolite in the ozonation process, an increase in the concentration of competing Fe2+ cations is permissible — 50 mg/dm3; Mn2+ — 100 mg/dm3 in solutions. The efficiency of extraction of Sr2+ and Mn2+ practically does not depend on the concentration of competing cations (Fe2+, Mn2+) in the drain water solutions.
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天然沸石的化学和矿物组成及其在核电厂污水臭氧化过程中的吸附性能
本文用同位素137Cs标记揭示了核电厂模型排水中有机组分的臭氧破坏和主要剂量形成核素(Cs -)仿制品吸附的全过程规律;Sokyrnytsky矿床的天然沸石(Co, Sr, Mn盐的稳定同位素)和吸附试剂化合物-亚铁和锰盐(II)。添加铁和锰盐臭氧化后的沸石的主要元素的化学组成实际上与天然沸石的组成没有什么不同。在含铁盐的臭氧化过程中,其物相组成以主要造岩矿物斜沸石和次生矿物石英为代表。沸石表面主要含铁相为针铁矿。次生相包括Fe(II)-Fe(III)层状双氢氧化物(绿锈)和绢云母,但相对含量不显著。对于沸石,在加入亚铁盐和锰(II)盐的臭氧氧化后,沸石的主要相为斜沸石和石英。沸石表面的含锰相主要为豪斯曼锰矿Mn3O4、氧化锰(II)和氧化锰MnO(OH)2。臭氧化过程中沉积在沸石表面的含铁相和含锰相主要表现为弱结晶或非晶化结构。形成剂量的放射性核素的主要吸附剂是沸石,而不是臭氧分解过程中在沸石表面形成的含铁和含锰的化合物。当Fe2+浓度增加到50 mg/dm3或Mn2+浓度增加到100 mg/dm3时,沸石对137Cs的最大吸附度可达90%。在初始典型竞争阳离子浓度(Fe2+ - 5 mg/dm3;Mn2+ - 10 mg/dm3),当Mn2+浓度增加到100 mg/dm3时。Sr2+和Mn2+的最大萃取度分别为99.4%和99.9%。为了使沸石在臭氧化过程中有效地提取137Cs和Co2+,可以增加竞争Fe2+阳离子的浓度- 50 mg/dm3;溶液中Mn2+ - 100mg /dm3。Sr2+和Mn2+的萃取效率实际上不取决于排水溶液中竞争阳离子(Fe2+, Mn2+)的浓度。
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0.70
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18
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