首页> 外文会议>ASME International Conference on Environmental Remediation and Radioactive Waste Management >APPLICATION OF AN ENVIRONMENTAL REMEDIATION METHODOLOGY: THEORY VS. PRACTICE REFLECTIONS AND TWO BELGIAN CASE STUDIES
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APPLICATION OF AN ENVIRONMENTAL REMEDIATION METHODOLOGY: THEORY VS. PRACTICE REFLECTIONS AND TWO BELGIAN CASE STUDIES

机译:环境修复方法的应用:理论与实践思考和两个比利时案例研究

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Like in many countries, polluted industrial sites also exist in Belgium. Although the contamination is purely chemical in most cases, they may also contain a radioactive component. For chemically contaminated sites, extensive regulations and methodologies were already developed and applied by the different regional authorities. However and essentially because radioactivity is a federal competence, there was also a necessity for developing a legal federal framework (including an ER-methodology [1]) for remediation of radioactive contaminated sites. Most of the so-called radioactive contaminated sites are exhibiting a mixed contamination (chemical and radiological), and hence the development of such methodology had to be in line with the existing (regional) ones concerning chemical contamination. Each authority having their own responsibilities with regard to the type of contamination, this makes it more complicated and time-consuming finding the best solution satisfying all involved parties. To overcome these difficulties the legal framework and methodology - including the necessary involvement of the stakeholders and delineation of each party's responsibilities - has to be transparent, clear and unambiguous. Once the methodology is developed as such and approved, the application of it is expected to be more or less easy, logic and straightforward. But is this really true? The aim of this document is to investigate as well the impact of factors such as the type of radioactive contamination - levels of contamination, related to NORM activity or not, homogeneous or heterogeneous, the differences in licensing procedures,... - on the application of the developed methodology and what could be the consequences in the long run on the remediation process. Two existing case studies in Belgium will be presented ([2]). The first case deals with a historical radium contaminated site, the second one with a phosphate processing facility still in operation, both with (very) low levels of radioactivity but containing very large volumes of contaminated materials. These case studies will demonstrate that, although the applied methodology will be the same in both cases, the impact of e.g. sampling strategy, scenario definitions, modelisations, final destination of the land, presence of chemotoxic components, dose or risk assessments, uncertainties, derivation of clean-up radionuclide guidelines, stakeholder involvement and waste treatment could be important on licensing, cost-estimate, planning and final outcome of the environmental remediation activities to be executed.
机译:像在许多国家,污染的工业用地也存在于比利时。虽然污染在大多数情况下,纯粹的化学,它们也可能含有放射性成分。对于化学污染的场所,广泛的法规和方法已经制定,并得到不同的区域主管机关实施。但是,基本上,因为放射性是一个联邦制的能力,也有制定一个法律框架,联邦(包括ER-方法[1])放射性污染场地修复的必要条件。大多数所谓的放射性污染地区都表现出混合污染(化学和放射性),因此这种方法的发展必须要与有关化学污染的现有(地区)的人行。有关于污染的类型,自己的责任。每个权限,这使得问题更加复杂,并找到满足所有相关方的最佳解决方案费时。为了克服这些困难的法律框架和方法论 - 包括利益相关者和各方责任划定必要的参与 - 必须是透明的,清晰和明确的。一旦该方法被开发为这样的批准,它的应用预计将或多或少容易,逻辑和简单。但这真的是真的吗?该文献的目的是调查以及的因素的影响,例如放射性污染的类型 - 污染的水平,与NORM活性或没有,均相或非均相,在许可程序的差异,... - 上的应用程序发达的方法和什么可能是在修复过程长远后果。在比利时两个现有案例研究将被呈现([2])。第一种情况涉及历史镭污染场地,第二个用磷酸盐处理设备仍然在操作中,都与放射性的(非常)低的水平,但含非常大量的被污染的材料。这些案例研究将证明,虽然应用的方法会在两种情况下是相同的,例如的影响抽样策略,情景定义,modelisations,土地的最终目的地,化学毒剂成分,剂量或风险评估,不确定性,清理放射性核素的指导方针,利益相关者参与和废物处理推导的存在可能是很重要的牌,成本估算,规划和要执行的环境整治活动的最终结果。

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