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压水堆核电站放射性废液的水泥固化研究 总被引:1,自引:0,他引:1
本文讨论了用水泥胶结剂固化压水堆含硼废液和酸碱去污液的适用性。碱性废液的固化不存在特殊困难。加氢氧化钠或偏铝酸钠进行中和及促凝可改善含硼废液和酸性去污液与水泥的化学兼容性,缩短浆体的凝固时间。添加30%斜发沸石可增加水泥固化体的机械强度、降低浸出率和减小固化体体积。 相似文献
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本文以沸石、硅灰、石英砂为添加剂,按照质量比m(沸石)∶m(硅灰)∶m(石英砂)∶m(水泥)=1∶1∶3∶10配方对模拟放射性含氟废液进行水泥固化。由配方得到的水泥浆流动度和初、终凝时间满足桶内固化要求。测定了水泥固化体28 d的抗压强度、抗浸泡性和抗冻融性实验后的强度损失,进行了抗冲击性能测试和模拟核素浸出实验。结果表明,该配方可有效地固化模拟放射性含氟废液,固化体28 d抗压强度、各项实验强度损失和模拟核素浸出率均满足GB 14569.1-2011的要求。水泥固化体的F-浸出率很低,XRD显示F-以CaF2形式存在。废液中F-质量分数控制在1%较为合适,此时水泥固化体终凝时间为14 h,F-的42 d浸出率为2.54×10-3 cm/d。 相似文献
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模拟非α中低放废液大体积浇注水泥固化的可行性研究 总被引:1,自引:0,他引:1
本文对在我国高放废液分离流程中产生的中低放非α废液的大体积浇注水泥固化,在实验室小试条件下进行了可行性研究。结果表明,经浓缩、脱硝及中和处理后,非低α中放废液可用大体积浇注水泥固化进行处理和处置。推荐的固化配方为:水灰比1.0 ̄1.1,盐灰比0.18 ̄0.20,及占水泥重量0.5%(wt)的水泥高效缓凝减水剂。固化体第42dCs的浸出率为10^-3 ̄10^-5cm/d,Sr的浸出率在3.1×10^ 相似文献
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放射性废液综合处理车间建成于2003年,其主要功能是通过蒸发浓缩处理中放废液,并最终将废液转化为水泥固化体进行永久处置。该车间生产能力为每天蒸发处理废液12t,生产水泥固化体15桶。该车间建成后,先后进行了冷试验和整改,使该车间具备了设计的生产运行能力,在2004年底,顺利完成了车间的热试验,热试验完成处理废液约100m^3,产生水泥固化体约40桶。 相似文献
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模拟放射性含硼废液的水泥固化研究 总被引:2,自引:1,他引:1
为了比较硫铝酸盐水泥和普通硅酸盐水泥含硼废液的固化,为配方优化提供依据,研究采用两种配方对模拟放射性含硼废液进行水泥固化。测定了固化体28d抗压强度、抗浸泡性、抗冻融性和耐γ辐照试验后的强度损失,进行了模拟核素浸出试验,并对固化体水化产物进行XRD分析。结果表明,两种配方可有效固化模拟含硼废液,固化体28d抗压强度、各项试验强度损失和模拟核素浸出率均满足GB14569.1—93的要求,试验所用的硫铝酸盐水泥配方对Cs+的滞留能力优于普通硅酸盐水泥配方,固化体中的硼以B(OH)4-形式固溶在钙矾石中。 相似文献
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针对某核电厂复杂成分的中、低放射性废液水泥固化体制备过程中出现的流动度损失快、泌水分层、凝结时间难控制等问题,通过实验研究掺合料、保水增稠材料、投料顺序等因素对放射性废液水泥固化体流动度、保水性能、凝结时间、固化体性能的影响规律。研制出既满足国家标准GB 14569.1—2011又适用于现有工程装置的放射性废液水泥固化体专用添加剂及配方,即专用添加剂配方为粉煤灰∶稠化粉∶外加剂A质量比=1∶1∶0.15,水泥固化体配方为水泥∶专用添加剂∶废液质量比=1∶0.272∶0.585。 相似文献
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中放废液大体积浇注水泥固化配方研究 总被引:2,自引:1,他引:1
本文研究了后处理厂中放蒸残液和元件脱壳的偏铝酸钠废液大体积浇注水泥固化的特殊工艺配方。实验用525普通硅酸盐水泥,模拟废液中分别含~(134)Cs 和~(85)Sr,其放射性浓度均为3.7×10(?)Bq/L。实验结果表明,选用加 DH 型水泥添加剂的配方可满足大体积浇注固化池内水泥浆“自流式”流平的技术要求,水泥浆的流动度达0.19m 以上;近似绝热养护后的中放蒸残液和偏铝酸钠废液固化体的抗压强度分别大于7.8和10MPa,固化体性能良好,近似绝热养护28天,两种固化体42天时~(134)Cs 和~(85)Sr 的浸出率均低于1.0×10~(-2)cm/d。 相似文献
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十年来低,中水平放射性废液处理技术的研究和发展 总被引:1,自引:0,他引:1
本文扼要地回顾了近十年来低、中放废液处理技术的研究和发展情况。目前,蒸发、离子交换和过滤等方法已广泛地用于处理废液。研究工作的重点是节能与提高效率。由于水泥和沥青固化方法的不足,废液固化研究是针对那些减容比高和固化物性能好的方法。在地质条件许可的情况下,操作简便和价格低廉的固化处置一体化方案已引起某些国家的关注。 相似文献
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To investigate the effect of borate on the cementation of radioactive evaporator concentrates, and to provide more data for solidification formula optimization, the simulated borate evaporator concentrates with different borate concentrations (as B) and Na/B ratio (molar ratio) were solidified by sulfoaluminate cement (SAC) and Portland cement (PC), with addition of Ca(OH)2, zeolite and accelerator or water reducer. The hydration products of solidified matrices were characterized by X-ray diffraction (XRD). The experimental results showed that borate retarded the cement setting for both SAC and PC formulas, and the final setting time prolonged with decrease of Na/B ratio. Borate could enhance the fluidity of the cement mixture. The 28 d compressive strengths of the solidified matrices for both SAC and PC formulas decreased with increase of borate concentration. The XRD patterns suggested that, in the matrices maintained for 28 d, borate did not interfere with the formation of main hydration products of SAC and PC. Borate, in the form of B(OH)4−, incorporated in ettringite (3CaO·Al2O3·3CaSO4·32H2O) as solid solution phase. The formula of SAC and PC developed in this study was effective for cementation of the simulated borate evaporator concentrates. However further optimization was required to reduce retarding effect of higher borate concentrations and to extend the practical feasibility for actual evaporator concentrates. 相似文献
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The necessity for and ways to improve the technology for reprocessing liquid radioactive wastes from nuclear power generation
are substantiated taking account of the chemical contaminants (petroleum products and products of corrosion). As a general
solution, it is proposed that autonomous modular purification facilities, operating on the principle of combining baromembrane
and sorption methods, be developed. The basic scheme of the proposed technology and the construction of the purification facilities
are described. The results of industrial tests performed on a tanker for collecting liquid wastes from the Pacific Ocean fleet
are presented. It is shown that purification to the level of allowed discharges into the sea is possible and that the radioactive
concentrates formed can be solidified by cementation.
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Translated from Atomnaya Energiya, Vol. 99, No. 4, pp. 283–289, October, 2005. 相似文献
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介绍了秦山核电基地在放射性废物最小化方面的实践。包括建立了蒸汽发生器排污树脂和通风过滤器金属框架清洁解控工作流程;改进了水泥固化线工艺,水泥固化包装容器采用金属桶代替水泥桶;开发了废过滤器芯子暂存衰变法分类处理及一桶装多芯方案;开发了技术废物“三明治”式废物装桶和超级压实提高外包装容器效率等最小化实践。对废液、废树脂、技术废物、有机废液等处理技术进行了比较分析,建议采用废液蒸干压实技术、废树脂蒸汽重整技术、可燃废物和有机废液焚烧技术,预计秦山核电基地废物产生量可由541 m3/a减至约94 m3/a。 相似文献
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A new approach to extracting cobalt(II) from non-borate and borate solutions of liquid radioactive wastes containing ligands
of ethylenediaminetetraacetate and oxalic acid is proposed. The approach is based on the difference in the stability of complexes
of organic ions with metals. Substituting iron(III) for cobalt results in almost complete liberation of Co2+ from the complex. Coprecipitation of Co2+ with Fe3+ in the form of oxohydroxides results in the liberation of Co2+ from solution into the solid phase. An excess of Fe3+ cations with respect to Co2+ and an increase of acidity, processing temperature, and aging time of the solutions at the preliminary stage results in complete
liberation of cobalt from the solution for pH ≥ 12. 相似文献
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AbstractAccording to the current planning status, radioactive waste with negligible heat generation is destined for storage in the Konrad waste repository in accordance with the Provisional Waste Acceptance Requirements(4). Waste of this kind occurs in the nuclear fuel cycle, research, medicine and technology. In its original state, the primary wastes of this type have various forms, such as: liquids, concentrates, sludges; ion exchange resins; compressible and/or combustible solids; incompressible solids, e.g. structural material components; filters, filter candles; other types of waste. The radioactive waste is appropriately conditioned and packaged before transport to the waste disposal site. To meet the basic requirements specified in the Waste Acceptance Requirements, primary waste must be solidified, for which the most common solidifying agents are cement and concrete although bitumen is also used. Waste products in decomposing, fermenting or liquid form or which contain a significant fraction in such states are not accepted for disposal. 相似文献
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本方法建立了磺胺甲恶唑酶联免疫分析方法用以检测动物源性食品中磺胺甲恶唑的残留。利用辣根过氧化物酶(HRP)标记SMX(Sulfamethoxazole ),兔抗SMX抗体制备固相抗体,通过标本中的SMX和一定酶标SMX竞争结合固相抗SMX多抗,标本中SMX的量和显色后的OD450值呈负相关的原理来检测标本中的SMX含量。经方法学鉴定,本方法的灵敏度为0.067μg/L,批内变异<10%,批间变异<20%。牛奶、肉类、鸡蛋、蜂蜜样品的回收率分别为94.9%~116.0%、 82.0%~107.6%、 81.6%~94.9%、89.0%~93.0%,符合免疫分析方法的要求, 相似文献