EGU General Assembly 2007 Neptune and Company, Inc. Los Alamos, NM, USA A Systems Modeling Approach for Performance Assessment of the Mochovce National.

Slides:



Advertisements
Similar presentations
Site Characterization Instructional Goal: Upon completion of this topic the participant will better understand the need to identify and evaluate various.
Advertisements

D:\data\PowerPoint\Maravic\NCP-EURATOM Meeting - CCAB ppt Slide 1 National Contact Points for EURATOM- Information Exchange Meeting October 16,
4/2003 Rev 2 I.1.1 – slide 1 of 13 Session I.1.1 Part I Review of Fundamentals Module 1Introduction Session 1Learning Objectives, Course Table of Contents.
2003 NGWA Midsouth Focus Conference September 2003 Neptune and Company, Inc. Modeling Uncertainty: Realism vs Conservatism in Radiological Performance.
Agent-based Modeling: A Brief Introduction Louis J. Gross The Institute for Environmental Modeling Departments of Ecology and Evolutionary Biology and.
Constellation Energy “The Way Energy Works” PWR Tritium Issues G. C. Jones.
Subsurface Fate and Transport of Contaminants
Introduction to SCREEN3 smokestacks image from Univ. of Waterloo Environmental Sciences Marti Blad NAU College of Engineering and Technology.
CE 510 Hazardous Waste Engineering
David O. Carpenter, MD Institute for Health and the Environment University at Albany.
RADIOACTIVE DISCHARGES CONTROL JE Jan Horyna State Office for Nuclear Safety Czech Republic September 2009 Vienna.
Phytotechnologies for Environmental Restoration and Management Micah Beard, M.S. Shaw Environmental, Inc.
Protection of the public and the environment standards? Rodolfo Avila.
1 WASTE CHARACTERIZATION METHODS S. Vanderperre Belgatom Vanderperre, Belgatom, chapter 7.
An increase of population and growth in economic development is causing adverse reactions with the surrounding environment of many areas. This population.
Exposure Assessment Thanks to Marc Rigas, PhD for an earlier version of this lecture Much of the materials is drawn from Paustenbach, DJ. (2000) The practice.
Interdisciplinary Modeling of Aquatic Ecosystems Curriculum Development Workshop July 18, 2005 Groundwater Flow and Transport Modeling Greg Pohll Division.
Environmental Health XIV. Standards and Monitoring Shu-Chi Chang, Ph.D., P.E., P.A. Assistant Professor 1 and Division Chief 2 1 Department of Environmental.
Environmentally Conscious Design & Manufacturing (ME592) Date: March 10, 2000 Slide:1 Environmentally Conscious Design & Manufacturing Class 3: Hazard.
Environmental Engineering
1 Risk Assessment Develop Objectives And Goals Develop and Screen Cleanup Alternatives Select Final Cleanup Alternative Communicate Decisions to the Public.
Decision analysis and Risk Management course in Kuopio
Michael H. Dong MPH, DrPA, PhD readings Human Exposure Assessment I (7th of 10 Lectures on Toxicologic Epidemiology)
IAEA International Atomic Energy Agency International Workshop on the Safe Disposal of Low Level Radioactive Waste WG3 debriefing.
Environmental Risk Analysis
Safety Assessment Methodologies and Implementation of Monitoring and Control Programmes Dr. Japie van Blerk AquiSim Consulting (Pty) Ltd Wednesday, 24.
College of Engineering Oregon State University DOE’s Graded Approach for Evaluating Radiation Doses to Biota: Derivation of Screening and Analysis Methodologies.
Exposure Assessment by Multi-media modelling. Cause-effect chain for ecosystem and human health as basis for exposure assessment by multi-media modelling.
Performance Assessment Issues in Waste Management and Environmental Protection Annual Meeting of the Baltimore-Washington Chapter of the Health Physics.
Ronald Warren Ecological & Environmental Monitoring National Security Technologies, LLC Community Environmental Monitoring Program Workshop July 26, 2011.
Case Study 1 Application of different tools: RBCA Tool Kit and APIDSS.
Production of Nitric Acid Environmental Impact Assessment Erik TolonenNick Poulin Environmental Engineering Environmental Planning and Decision Making.
Chapter 11 Environmental Performance of a Flowsheet.
United States Nuclear Regulatory Commission 1 Simulation Modeling: A Reviewer’s Perspective David W. Esh 1 and Cynthia S. Barr 2 Division of Waste Management.
Intervention for Chronic and Emergency Exposure Situations Assessment and Response during Radiological Emergency Dose Assessment Overview Lecture IAEA.
1 Probabilistic Scenario Analysis (PSA) 2 PSA -History In 1940’s - work on the atomic bomb In the 1950's - used as "what if" scenarios for nuclear proliferation.
Nicolas Solente Workshop on Regulatory Requirements to Ensure Safe Disposal of Disused Sealed Sources for Operators and Regulators Amman, JORDAN 7-11 April.
IAEA International Atomic Energy Agency Summary and Overview of TECDOC Russel Edge Decommissioning and Remediation Unit Division of Radiation,Transport.
Evaluation of the radiological consequences of tritium present in radioactive components from fusion reactors Task TW4-TSW-001-D1b: Waste and decommissioning.
A Systems’ Approach to the Design of a Methodology and Mathematical Model for Determining the Most Critical Links of a Highway Network Gerard Ibarra PhD.
Reclaimed Wastewater Quality Criteria, Standards, and Guidelines
1 Current Issues in Siting Safety Reviews Michelle Hart, Sr. Reactor Engineer Division of Site and Environmental Reviews NRC Regulatory Information Conference.
Working With Simple Models to Predict Contaminant Migration Matt Small U.S. EPA, Region 9, Underground Storage Tanks Program Office.
Probabilistic Modelling Golder Associates (UK) ltd Ruth Davison Attenborough House Browns Lane Stanton on the Wolds Nottingham NG12 5BL
DOE ENVIRONMENTAL PROTECTION PROGRAM WORKSHOP BIOTA PROTECTION Stephen L. Domotor (202)
-1- UNRESTRICTED / ILLIMITÉ Demonstrating the Safety of Long-Term Waste Management Facilities Dave Garrick 2015 September.
AGU Fall 2006 Meeting Neptune and Company, Inc. Radioactive Waste Disposal in Hydrologically-Challenged Environments: Opportunities for Waste Disposal.
Types of Models Marti Blad Northern Arizona University College of Engineering & Technology.
International Atomic Energy Agency Regulatory Review of Safety Cases for Radioactive Waste Disposal Facilities David G Bennett 7 April 2014.
Safety-related Issues for the Disposal of Intermediate Level Waste (ILW) Dr. Jürgen Wollrath Federal Office for Radiation Protection (BfS) Department Safety.
Waste and site related issues Fredrik Vahlund SKB.
NUATRC/TCEQ Air Toxics Workshop October Air Toxics Air Toxics: What We Know, What we Don’t Know, and What We Need to Know Human Health Effects –
IAEA International Atomic Energy Agency Presenter Name School of Drafting Regulations for Borehole Disposal of DSRS 2016 Vienna, Austria Siting Strategies.
1 Modeling Complex Systems – How Much Detail is Appropriate? David W. Esh US Nuclear Regulatory Commission 2007 GoldSim User Conference, October 23-25,
INTRODUCTION TO ENVIRONMENTAL MODELING. EIA Scientific Tools and Techniques2 Lesson Learning Goals At the end of this lesson you should be able to: 
IAEA International Atomic Energy Agency TM Technical Meeting to Discuss Human Intrusion and Future Human Actions in relation to Disposal of Radioactive.
“ Building Strong “ Delivering Integrated, Sustainable, Water Resources Solutions Uncertainty & Variability Charles Yoe, Ph.D.
Danyl Pérez Sánchez CIEMAT-SPAIN
Structure of a Safety Case (NEA). The Multibarrier Concept each barrier acting passively in concert with the others to isolate, contain and reduce impacts.
ALARA IMPLEMENTATION AT UKRAINIAN NPPs T. Lisova, Nuclear Energy Department, Ministry of Fuel and Energy of Ukraine Y. Roshchyn, National Nuclear Energy.
Risk CHARACTERIZATION
Use and Conduct of Safety Analysis IAEA Training Course on Safety Assessment of NPPs to Assist Decission Making Workshop Information IAEA Workshop Lecturer.
Exposure Modelling Day 1.
Module 17: MIXING ZONES A limited area or volume of water where initial dilution of a discharge takes place and where numeric water quality criteria.
Plenary Meeting of the Network on  Environmental 
Introduction: IAEA activities / Documents on human intrusion
Addressing Future Human Actions for Safety Assessment
Apes Ch 11 Risk, Toxicology, and Human Healthy
SAFRAN Upgraded to support the implementation of the Borehole Disposal Concept Rodolfo Avila, Facilia AB.
Modeling Water Treatment Using the Contaminant Transport Module
Presentation transcript:

EGU General Assembly 2007 Neptune and Company, Inc. Los Alamos, NM, USA A Systems Modeling Approach for Performance Assessment of the Mochovce National Radioactive Waste Repository, Slovak Republic John Tauxe, PhD, PE Paul Black, PhD Václav Hanušík VÚJE, Inc. Trnava, Slovakia

EGU General Assembly 2007 Presentation Outline physical system modeling introduction to the facility conceptual system model mathematical model computer model future work

EGU General Assembly 2007 What is the problem? Radioactive wastes exist. Sources: nuclear power, nuclear medicine, industry, and (in some countries) nuclear weapons They pose a long-term health hazard. At risk: workers, the general public, the environment How should they be managed? Considerations: worker exposure, containment, release to the environment, future harm reduction

EGU General Assembly 2007 Why use modeling? Models provide insight into the problem. Important processes can be identified. The effects of uncertainty can be quantified. Models help to evaluate alternatives. Cost/benefit of alternatives can be performed. Relative effectiveness can be evaluated. Models communicate technical issues. Transparent modeling is accessible to the public. Visualization of processes increases understanding.

EGU General Assembly 2007 Are models too abstract to be of use? “Essentially all models are wrong... We know that none of the results are correct per se, though we have defined an envelope of plausible estimates, conditioned on knowledge....but some are useful.” ¹ We gain insight into what is important, and can demonstrate relative effects of mitigation (of doses, for example). ¹ Box, George E. P.; Norman R. Draper (1987). Empirical Model-Building and Response Surfaces, p. 424

EGU General Assembly 2007 Physical System Modeling Overview a radioactive waste disposal facility in Tennessee USA Near field: Radiological materials leak out of stacked concrete vaults. example: Human and ecological health effects arise from exposure to contaminants transported through an engineered (near field) and natural (far field) environment to a biological (physiological) environment Far field: Contaminants migrate through geologic materials. Physiological exposure: Human or ecological receptors are exposed by several pathways.

EGU General Assembly 2007 Physical System Processes Near field: decay / ingrowth advection / dispersion diffusion dissolution precipitation containment degradation The processes involved in this exposure modeling are radiological, physical, chemical, geological, and biological. Far field: decay / ingrowth advection / dispersion dilution colloidal transport chemical transformation biological uptake and translocation Physiological exposure: habitation drinking water eating plant and animal foodstuffs breathing pharmacokinetics and dose response These (and more) can be modeled in any degree of detail. An important question: What degree of detail is appropriate?

EGU General Assembly 2007 Mathematical Coupling of Modeled Processes Physical processes are modeled as coupled partial differential equations: radioactive decay and ingrowth gaseous diffusion aqueous diffusion aqueous advection soil/water chemical partitioning air/water partitioning chemical solubility atmospheric resuspension

EGU General Assembly 2007 System Modeling model input parameters modeled processes modeling results average annual precipitation = N(  =55 cm,  =35 cm ) examples: time dose water movement follows Darcy’s Law:

EGU General Assembly 2007 Location Map for Mochovce, Slovakia Wein (Vienna) Bratislava Mochovce

EGU General Assembly 2007 Repository in a Small Watershed Wein (Vienna) Trnava Bratislava Mochovce

EGU General Assembly 2007 Inside a Vault Structure

EGU General Assembly 2007 The Mochovce GoldSim Model

EGU General Assembly 2007 Computer Modeling in GoldSim* materials are defined (Water, Soil, etc.) compartmentalization of model domain uses Cell and Pipe elements connections between compartments define transport pathways Source elements contain initial radionuclide inventory (Species) contaminants disperse along pathways calculations are done through time GoldSim is natively probabilistic * Information about GoldSim™ is available from

EGU General Assembly 2007 Engineering Design Near Field

EGU General Assembly 2007 Near Field Calculations

EGU General Assembly 2007 Repository Far Field Environment repository stream to lake Mochovce NPP

EGU General Assembly 2007 Far Field Calculations

EGU General Assembly 2007 Typical Results Any state or condition of the model can be tracked and graphed through time (e.g. concentrations, flow rates, doses). This could be concentration or dose.

EGU General Assembly 2007 Managing Uncertainty We know that our knowledge is incomplete. Of that we are certain. How can we allow and account for imperfect knowledge? Each modeling parameter and process has inherent uncertainty and variability, and therefore so must our results. no single answer is correct a collection of answers reflects our knowledge time dose time dose

EGU General Assembly 2007 Why Probabilistic Modeling? Uncertainty Analysis UA allows a more honest answer, based on our state of knowledge. Sensitivity Analysis SA provides insight into which modeling aspects (parameters and processes) are important.

EGU General Assembly 2007 Probabilistic Analysis modeling parameters are defined stochastically, capturing uncertainty Monte Carlo is handled by GoldSim sensitivity analysis performed on results using the open source R software sensitive parameters are identified value-of-information analysis performed revisions through Bayesian updating

EGU General Assembly 2007 Future Work Extensions Performance assessment modeling can be extended to help with worker safety facility design optimization of operations development of waste acceptance criteria efficient use of monetary resources

EGU General Assembly 2007 Conclusions Thoughtful stochastic physical system modeling can capture our state of knowledge. Defensible and transparent decisions can be made using such models. A system model can do much more than radiological performance assessment (worker risk, optimization, cost/benefit).

EGU General Assembly 2007 Mochovce, Slovakia repository This presentation can be found here: