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ICEM11 Final Program 9.7.11pm_ICEM07 Final Program ... - Events

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Session 9 Abstracts<br />

5) ENVIRONMENTAL SURVEILLANCE SYSTEM FOR THE SHCHUCHYE SITE (wP-59042)<br />

Stephane Belbeze, Matthieu Hallouin, Antea (France)<br />

An intergovernmental agreement on cooperation about chemical weapon destruction was signed between France and the Russian<br />

federation on 14th February 2006 in the context of a Global Partnership dedicated to preventing catastrophic terrorism and the<br />

proliferation of weapons of mass destruction. It came into effect on 25th April 2007 after ratification by both countries. The present<br />

demonstrated project was launched as part of this collaboration on the Shchuchye site (Russia – Kurgan Oblast). The project<br />

concerned the environmental surveillance system for the Shchuchye site required for the safe operation of the installation used to<br />

destroy chemical weapons.<br />

The aim was to implement equipments and methods of analysis for very low concentrations of pollutants in the three environmental<br />

compartments: air, water and soil. This has been achieved with the help of industry and other organizations in France (Environment/SA<br />

for supplies, INERIS and Antea Group) and Russia (ROST Association and EKROS Engineering). This system takes<br />

account of the normal operation of the installation as well as incident management. It includes 11 stationary atmospheric measuring<br />

stations constructed by Environment/SA and EKROS Engineering including ASTEK dedicated toxic gas detector : “Terminator<br />

FOV-1”, 3 mobile atmospheric measuring stations, 2 mobile soil & water measuring stations, 4 sampling cars constructed by<br />

Environment/SA and EKROS Engineering, a complete Chemical analysis laboratory which can handle ppb analysis of toxic gases,<br />

organics and minerals pollutants, an information collection center and a meteo station which can retrieve, display and archive all<br />

the datas or alarm from the stationary and mobile stations. Antea Group has provided a technical expertise and various negotiations<br />

during the negotiation phase, the project initiation files & contracts redaction, the project Monitoring and reporting to stakeholders,<br />

the REX. Up to 2009, No other site of the world uses such an innovative system. Antea Group worked on this project for 4<br />

years. It successfully began operating in March 2009, before the start of destruction operations, after 15 months of work on the site.<br />

6) 25 YEARS AFTER CHERNOBYL NPP ACCIDENT: EXPERIENCE AND TRENDS OF RADIOACTIVE<br />

CONTAMINATED SOILS REHABILITATION IN BELARUS (wP-59242)<br />

Leanid Maskalchuk, JIPNR-Sosny NAS of Belarus (Belarus)<br />

The paper describes the developed and applied soil decontamination measures and methods in Belarus after the Chernobyl<br />

NPP accident. It is considered the possibility of using of organomineral amendments based on natural raw materials (sapropel)<br />

and industrial wastes (hydrolyzed lignin, clay-salt slimes) for rehabilitation of radioactive contaminated soils.<br />

SESSION 9 — POSTER SESSION: LOW/INTERMEDIATE LEVEL WASTE MANAGEMENT (1.1)<br />

1) NUMERICAL MODELING FOR COLLOID-FACILITATED MIGRATION OF N-NUMBER<br />

RADIONUCLIDES CHAINS IN THE FRACTURED ROCK (w/oP-59257)<br />

Chun-Ping Jen, National Chung Cheng University (Taiwan)<br />

A previous numerical model for N-member radionuclide decay chains has been extended to include the effect of radionuclide<br />

sorption with groundwater colloids. Published distribution coefficients were employed in the nuclide decay chain to illustration the<br />

present model. The colloid concentration was assumed constant in time and space owing to equilibrium between colloid generation<br />

and sedimentation by chemical and/or physical perturbations. Furthermore, the diffusion of colloids into the rock matrix was<br />

ignored because the diameter of colloid is relatively large and colloids and fracture surfaces are like-charged. The results indicated<br />

that colloids could facilitate the transport of radionuclides and the large adsorbability of nuclides with colloids enlarged the effect<br />

of acceleration by colloids. The influence of colloids on the radionuclide transport was expected to be crucial to the actinides with<br />

large adsorbability; however, the present results revealed that the low-adsorbing nuclides whose parent nuclides have large capability<br />

of sorption could be also facilitated significantly by colloids indirectly. Therefore, the role of colloids played in the transport<br />

of the radionuclides decay chain should be assessed carefully in the radioactive waste disposal. The numerical method presented<br />

herein is helpful to verify/validate further complex far-field models.<br />

2) LABORATORY EXPERIMENTS ON THE ALTERATION OF HIGHLY-COMPACTED BENTONITE BY<br />

ALKALINE SOLUTION AND THE EFFECTS ON PHYSICAL PROPERTIES (wP-59318)<br />

Satoru Miyoshi, Shinya Morikami, Yukinobu Kimura, Tomoko Jinno, Shuichi Yamamoto, Obayashi Corporation (Japan)<br />

The issue has to be considered for the evaluation of performance of multiple burrier systems in geological repository of<br />

radioactive waste wheather alkaline leachate from cement matterials may alterate clay materials so that they can not show the<br />

required performance. In order to study on the alkali alteration of compacted bentonite and the effect on the physical properties,<br />

using modified consolidation apparatus, we have done a series of experiments for a long term such that alkali solution is injected<br />

into compacted bentonite to measure the temporal change of swelling pressure, flow rate, and the compositions of outflow solution.<br />

We settled two cases for the experiment: one is the case where 1.0 mol/L sodium hydroxide solution is injected (case 1) and<br />

the other saturated calcium hydroxide solution (case 2). The dry density of specimen for both cases are 1.6 g/cm3. The dissolution<br />

of the minerals in the high-pH environment is mainly considered in case 1 and the effect of the secondary minerals to be generated<br />

in calcium rich environment is mainly considered in case 2. The experiment is done in the bath with constant temperature 70<br />

celcius degree to reasonably accelerate the reaction of alkali alteration. In addition to the above measurements, a series of analysis<br />

of solid phase is done after one and half year injection of alkaline solution. Through the experiment, we found that the dissolution<br />

rate of montmorillonite is much lower than those of accompanying minerals and that the physical properties are reasonably kept<br />

even though some part of the minerals are dissolved.<br />

64

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