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June 25-26, 2002 D&D Lessons Learned Workshop 1 Tritium Decontamination Techniques and Technology C. A. Gentile, J. J. Parker D&D Lessons Learned Workshop June 25-26, 2002 PPPL

June 25-26, 2002D&D Lessons Learned Workshop1 Tritium Decontamination Techniques and Technology C. A. Gentile, J. J. Parker D&D Lessons Learned Workshop

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June 25-26, 2002 D&D Lessons Learned Workshop 1

Tritium Decontamination Techniques and Technology

C. A. Gentile, J. J. ParkerD&D Lessons Learned Workshop

June 25-26, 2002

PPPL

June 25-26, 2002 D&D Lessons Learned Workshop 2

Oxidative Chemistry Employed for Tritium Removal

1. H2O2 (hydrogen peroxide) liquid phase

2. O3 (ozone) gas phase

Technology Overview• Reduce tritium surface (and bulk) contamination on various

components and items

• Remove contamination by chemically reacting elemental T to tritium oxide (purge reaction effluent to TCS or stack)

• Control via implementation of specific concentrations, catalytic parameters, and/or process conditions

June 25-26, 2002 D&D Lessons Learned Workshop 3

Introduction

• Expendable items de-tritiated to activity levels at or slightly above background level

• Re-usable items de-tritiated to free release levels (< 1000dpm/100cm2, and for use in controlled areas)

• Oxidative Tritium Decontamination System (OTDS) capital cost and operation cost is relatively low, compared to other decontamination methods

June 25-26, 2002 D&D Lessons Learned Workshop 4

Background

• O3 and H2O2 decontamination processes both employ oxidative chemistry

• Process was implemented on contaminated RF Feedthrough components (copper, stainless steel)

• Post H2O2 process activity levels dropped significantly (< 1% initial activity)

• No discernable surface regrowth was noted after approximate 8 month hold time

June 25-26, 2002 D&D Lessons Learned Workshop 5

Background

Stainless Steel RF Feedthrough

Components

Copper Internal Conductor Component

June 25-26, 2002 D&D Lessons Learned Workshop 6

Background

June 25-26, 2002 D&D Lessons Learned Workshop 7

System Configurations

Oxidative Tritium Decontamination System

Rotary Stationary

June 25-26, 2002 D&D Lessons Learned Workshop 8

Rotary System Configuration

June 25-26, 2002 D&D Lessons Learned Workshop 9

Stationary System Configuration

June 25-26, 2002 D&D Lessons Learned Workshop 10

Piston-Cylinder Configuration

Vo = XCo = [O3] Vf = 0.5X

Cf = 2[O3]

uncompressed compressed

June 25-26, 2002 D&D Lessons Learned Workshop 11

Reaction Chemistry

June 25-26, 2002 D&D Lessons Learned Workshop 12

• Secondary reactions (promote additional release of hydrogen isotopes) • oxidation of carbon via ozone and/or diatomic oxygen to yield

CO2 (and CO)

• reaction of nitrogen (if present in system) with tritium to yield tritiated ammonia

• oxidative dissociation of polymer chains

Reaction Chemistry

June 25-26, 2002 D&D Lessons Learned Workshop 13

• Required duration of O3 exposure dependant upon:• concentration of pure O3 in feed

• residence time in reaction chamber

• These parameters are controlled via the following:• concentration of diatomic oxygen in gaseous supply to ozone

generator

• volumetric flow rate (output) of ozone generator

• volume of reaction chamber

Reaction Chemistry

June 25-26, 2002 D&D Lessons Learned Workshop 14

• Desiccation/drying of feed supply• Lowers relative humidity within reaction chamber, thus facilitating

evaporation of HTO (tritium oxide)

• Reduces possibility of formation of hydroxyl radicals, which can hinder the primary reaction mechanism

Desiccation/drying of feed supply yields shorter system run-time

Reaction Chemistry

June 25-26, 2002 D&D Lessons Learned Workshop 15

Decomposition of Excess Ozone Following Oxidation Process in OTDS

• HVAC ductwork, in most cases, is constructed of ferrous metal, which exhibits corrosion when exposed to strong oxidizing agents

• Ozone will degrade polymer-composite seals present in HVAC systems

• It is necessary to significantly reduce the release of ozone into these systems

June 25-26, 2002 D&D Lessons Learned Workshop 16

Decomposition of Excess Ozone Following Oxidation Process in OTDS

• Thermal Decomposition

• Activated Carbon Decomposition

• Hopcalite Catalyst Decomposition

June 25-26, 2002 D&D Lessons Learned Workshop 17

Thermal Decomposition

Ozone must be held at temperatures exceeding 300 degrees Celsius for an approximate 3 second duration for adequate conversion to occur

June 25-26, 2002 D&D Lessons Learned Workshop 18

Activated Carbon Decomposition

Design of activated carbon bed must allow for an approximate 3 second residence time for adequate conversion to occur

June 25-26, 2002 D&D Lessons Learned Workshop 19

Hopcalite Catalyst Decomposition

• MnO2 (manganese dioxide) based catalyst

• Not consumed during ozone decomposition

• Approximate 0.36-0.72 second residence time

• >99% conversion of up to 120000 ppm ozone

June 25-26, 2002 D&D Lessons Learned Workshop 20

Efficient Removal of HTO

• HTO formed via this reaction mechanism is not removed through chemical process

• Majority of HTO remains as condensate on material surfaces

• A physical process (i.e. evaporation) must be implemented to facilitate HTO removal

June 25-26, 2002 D&D Lessons Learned Workshop 21

Efficient Removal of HTO

June 25-26, 2002 D&D Lessons Learned Workshop 22

Results

June 25-26, 2002 D&D Lessons Learned Workshop 23

Results