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Mathematical Models for Assessing Remediation of Radioactively - - PowerPoint PPT Presentation

Mathematical Models for Assessing Remediation of Radioactively Contaminated Sites IAEA TECDOC under development Rodolfo Avila, Facilia AB Horst Monken-Fernandes, IAEA Brent Newman, IAEA Jiri Simunek, University of California George Yeh,


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Mathematical Models for Assessing Remediation of Radioactively Contaminated Sites

IAEA TECDOC – under development

Rodolfo Avila, Facilia AB Horst Monken-Fernandes, IAEA Brent Newman, IAEA Jiri Simunek, University of California George Yeh, University of Central Florida Charley Yu, Argonne National Laboratory

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Table of Contents

  • INTRODUCTION
  • CONCEPTUAL MODELS
  • SOURCE TERM MODELS
  • ATMOSPHERIC DISPERSION MODELS
  • VADOSE ZONE MODELS
  • GROUNDWATER MODELS
  • INTEGRATED SUB-SURFACE MODELS
  • SURFACE WATER MODELS
  • EXPOSURE ASSESSMENT
  • APPLICATION FOR DECISION MAKING IN ENVIRONMENTAL

REMEDIATION

  • ASSESSMENT OF REMEDIATION SOLUTIONS
  • DEMONSTRATIVE EXAMPLES
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CHAPTER 2 – CONCEPTUAL MODELS

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SOURCE ATMOSPHERE VADOSE GROUNWATER LAND SURFACE SURFACE WATER WELL

Release Groundwater transport Deposition Leaching Discharge Abstraction Irrigation CONTAMINATED AREA RECEPTOR LOCATION Deposition Surface runoff Recharge Release Atmospheric dispersion

Main transport pathways

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Processes influencing the radionuclide transport

ATMOSPH Rainfall Dry deposition Gas uptake Rainfall Dry deposition Gas uptake Rainfall Dry deposition Gas uptake Resuspension Volatilization/ Emanation Evaporation Transpiration Source Percolation Advection Diffusion Dispersion Colloid transp. Erosion Surface runoff Sedimentation Vadose Recharge Advection Diffusion Dispersion Colloid transp. Capillary rise Advection Diffusion Colloid transp. GW Discharge/Seepage Pumping Resuspension Volatilization/ Emanation Evaporation Transpiration Inflitration Advection Diffusion Dispersion Colloid transp. LAND SURFACE Surface runoff Recharge Irrigation Flooding SURFACE WATER Irrigation Well

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Processes in the source, the vadoze, the groundwater and the surface land compartments

INPUT AQUEOUS Adsorption / Surface complexation Ion exchange Precipitation Volatilization Heterogeneous reaction Diffusion Decay (Rn, Tn) Desorption Ion exchange SOLID Co‐precipitation Decay (Rn, Tn) Dissolution Co‐precipitation SUSPENDED Decay (Rn, Tn) Condensation Diffusion Decay (Rn, Tn) Decay (Rn, Tn) Decay (Rn, Tn) GASEOUS MICROBES OUTPUT

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Exposure pathways

On-Site Direct Exposure On-Site Air Concentration Dust/ H-3 Radon Plant Foods Livestock Meat Milk Aquatic Foods On-Site Water Contamination On-Site Soil Contamination External Radiation Ingestion Effective Dose Equivalent/ Excess Cancer Risk to an Exposed Individual

Residual Radioactive Material In Soil

Source Environmental Pathway Exposure Pathway Dose or Cancer Risk

Inhalation On-Site Biotic Contamination On-Site Direct Exposure On-Site Air Concentration Dust/ H-3 Radon Plant Foods Livestock Meat Milk Aquatic Foods On-Site Water Contamination On-Site Soil Contamination External Radiation Ingestion Effective Dose Equivalent/ Excess Cancer Risk to an Exposed Individual

Residual Radioactive Material In Soil

Source Environmental Pathway Exposure Pathway Dose or Cancer Risk

Inhalation On-Site Biotic Contamination

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Interactions between models

ATMOSPHERIC DISPERSION SURFACE RUNOFF SOURCE TERM VADOSE GROUNDWATER SURFACE WATER

Release to surface water Release to Vadose Release to Groundwater Release to Surface waters Deposition Release to atmosphere Conc Air Deposit Conc Water Conc Food Conc Sediment Conc Well Water

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CHAPTER 3 SOURCE TERM MODELS

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SOURCE TERM MODELS 3.1 Introduction 3.2 Simplified assessment (equilibrium) models 3.2.1 Release to the atmosphere 3.2.2 Release to the vadose zone/groundwater 3.2.3 Release to surface water bodies 3.2.4 Applicability of the models and information required

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3.3 Biogeochemical models All biogeochemical models are based on the principle of mole balances and principle of thermodynamics for fast/equilibrium reactions and chemical kinetics for slow/kinetic reactions. 3.3.1 Release to the Atmosphere 3.3.2 Release to the vadose zone/groundwater 3.4 Uncertainties associated with these models

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CHAPTER 4 ATMOSPHERIC DISPERSION MODELS

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The main focus of this Chapter will be on describing how to apply these models for the case of area sources. A simple approach, proposed in the IAEA SR 19, is to calculate a pseudo point source release rate by integrating over the entire area of the source and locating the release point at the edge of the area nearest to the location of the receptor of

  • interest. A more sophisticated approach is to divide the area

into several cells and perform calculations for each cell. A Table with a description of available models will be

  • included. An example is the Argonne model MILDOSE.

A description of how to estimate the concentrations needed for the exposure assessment will be also included.

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4.1 Introduction 4.2 Continuous long-term releases 4.3 Short term releases 4.4 Application of the models and information required

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CHAPTER 5 VADOSE ZONE MODELS

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5.1 Introduction 5.2 Simplified assessment (equilibrium) models 5.2.1 Applicability of the models and information required 5.3 Flow and transport models 5.3.1 Water flow 5.3.2 Solute transport 5.3.3 Soil hydraulic properties 5.3.3.1 Retention Curve 5.3.3.2 Hydraulic Conductivity 5.3.3.3 Pedo transfer Functions 5.3.4 Transport properties 5.3.5 Applicability of the models and information required

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5.4 Biogeochemical models Geochemical models: Wateq, Minteq, Geochemist Workbench, PHRE

  • Geochemical transport models: PHREEQC, HP1,

HydroBioGeoChem, others 5.5 Uncertainties associated with these models

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CHAPTER 6 GROUNDWATER MODELS

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6.1 Introduction 6.2 Simplified assessment models This section will include description of analytical equations and simple compartment models that can be used for estimating the transport of radionuclides with groundwater. 6.2.1 Applicability of the models and information required 6.3 Flow and transport models 6.3.1 Media hydraulic properties 6.3.2 Transport properties 6.3.3 Applicability of the models and information required 6.4 Biogeochemical models Table of models (e.g., MODFLOW, RT3D, MT3D, MODFLOW Surfact, FeFlow, Porflow, HYDRUS) 6.5 Uncertainties associated with these models

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CHAPTER 7 INTEGRATED SUB-SURFACE MODELS

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7.1 Introduction 7.2 Flow and transport models 7.3 Biogeochemical models 7.4 Applicability of the models and information required 7.5 Uncertainties associated with these models

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CHAPTER 8 SURFACE RUNOFF MODELS

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8.1 Introduction 8.2 Simplified assessment (equilibrium) models Surface runoff using Universal Soil Loss Equation will be

  • presented. The model to estimate radionuclide concentrations and

dilution in surface water body will be presented. 8.2.1 Applicability of the models and information required The data required in the model and the limitations of the model will be discussed. 8.3 Flow and water quality transport models 8.3.1 Applicability of the models and information required 8.4 Uncertainties associated with these models

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CHAPTER 9 SURFACE WATER MODELS

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This section provides guidance on how estimate concentrations in surface waters from the releases obtained with the models described in the previous sections. A full description of the models will not be included but rather advice will be provided on how to use the models in the IAEA SR 19. 9.1 Introduction 9.2 Simplified assessment models 9.2.1 Lakes 9.2.2 Rivers 9.2.3 Estuaries 9.2.4 Coastal areas 9.3. Uncertainties associated with these models

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CHAPTER 10 EXPOSURE ASSESSMENT

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10.1 Introduction 10.2 External exposure 10.2 Inhalation 10.3 Ingestion 10.3.1 Water 10.3.2 Food 10.3.3 Soil

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CHAPTER 11 APPLICATION FOR DECISION MAKING IN ENVIRONMENTAL REMEDIATION CHAPTER 12 ASSESSMENT OF

REMEDIATION SOLUTIONS

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CHAPTER 13 DEMONSTRATIVE EXAMPLES

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13.1 Uranium Tailings An uranium tailings simulation in the integrated subsurface media will be provided. Assessment of remediation strategies of uranium tailing for a legacy site in Dnieprozerchinsk, Ukraine. 13.2 In situ leaching An in-situ leaching (natural monitored attenuation) simulation in integrated subsurface media will be proved. 13.3 Acid drainage An acid drainage example in integrated subsurface media will be

  • provided. Application of a water flow and geochemical modeling to

support the remediation activities of the acid rock drainage generation in the uranium mining and milling site of Pocos de Caldas Brazil 13.4 Application of isotope techniques