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atw - International Journal for Nuclear Power | 04.2023

Umwelt, Klima, Energiesysteme Betriebsergebnisse 2022

Umwelt, Klima, Energiesysteme
Betriebsergebnisse 2022

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<strong>atw</strong> Vol. 68 (2023) | Ausgabe 4 ı Juni<br />

Dynamic Dispersion Modelling to<br />

Enable In<strong>for</strong>med Decision Making<br />

in a Modern <strong>Nuclear</strong> Safety Case<br />

Howard Chapman, Joseph Hargreaves, Stephen Lawton, Robert Gordon, Tim Culmer<br />

Introduction<br />

Radionuclide material when discharged into the atmosphere<br />

is carried along by the wind and dispersed<br />

into the environment by the action of turbulent diffusion<br />

[1] . As outlined by Hester and Harrison “the<br />

problem of predicting the distribution of airborne material<br />

released from a source is commonly approached<br />

by solving the diffusion-transport equation. There are<br />

a range of models which have been developed to solve<br />

the equation depending upon simplifying assumptions<br />

made and boundary conditions imposed” [2] .<br />

The National <strong>Nuclear</strong> Laboratory (NNL) have historically<br />

used computer modelling techniques which<br />

are based upon the National Radiation Protection<br />

Board (NRPB) Model <strong>for</strong> Short and Medium Range<br />

Dispersion of Radionuclides Released to the Atmosphere,<br />

NRPB-R91 [1] , and Near Wake Modelling,<br />

NRPB-R157 [3] . These approaches are based on a<br />

simplified Gaussian model; but, as with most dispersion<br />

models, there are limitations on the range at<br />

which the model can be appropriately used because<br />

the modelling technique uses weather data from the<br />

release point <strong>for</strong> the whole release path. Other factors<br />

affecting the model can include release height,<br />

topography and deposition, amongst others.<br />

Riskaware have developed an assessment code called<br />

the Urban Dispersion Model (UDM) which estimates<br />

the downwind dispersion of airborne contaminants.<br />

This higher fidelity model can predict atmospheric<br />

transport and dispersion of chemical, biological and<br />

radiological materials within urban and semi-urban<br />

environments, including modelling the effects<br />

of buildings, wake regions, courtyards, and urban<br />

canyons. UDM also models complex material effects<br />

such as wet and dry particulate deposition, primary<br />

and secondary liquid evaporation, and buoyant and<br />

dense gas modelling.<br />

As the need to respond to climate change leads to<br />

renewed interest in the potential <strong>for</strong> new nuclear<br />

energy and deployment as co-generation sites (i.e.<br />

where the heat energy from the reactor is used <strong>for</strong><br />

multiple purposes such as electricity, district heating,<br />

process heat and hydrogen/chemical production) it<br />

becomes important to start considering both the radiological<br />

and chemical hazards in a more rounded<br />

way. Traditionally, nuclear Safety Cases have focused<br />

predominately on the radiological hazards associated<br />

with the site; and where required assessment of<br />

specific chemical hazards are undertaken when the<br />

facilities in question contained significant quantities<br />

of certain hazardous and/or toxic chemicals.<br />

However, as the likelihood of co generation looks<br />

to become a reality there is a need to consider all<br />

hazards related to the activities on a site in a more<br />

complete manner. It is considered that use of UDM<br />

in the nuclear industry could provide a unique opportunity<br />

to improve the assessment of radiological<br />

and chemical aerial release hazards. The approach<br />

would allow safety assessors to compare the consequences<br />

of radiological and chemical hazards in<br />

the same code making it easier and more effective<br />

to balance the risks associated with a facility and<br />

any neighbouring major accident hazard sites in a<br />

more holistic way.<br />

Proposed Future Application of UDM<br />

The aim of this paper is to provide an overview of<br />

the current position regarding dispersion modelling<br />

and how this might be improved by the use of the<br />

Riskaware UDM to support dispersion calculations<br />

in consequence assessment and Safety Case work.<br />

It is also thought that using the enhanced graphical<br />

outputs, provided by the UDM interface, will assist<br />

the engagement process with Regulators and other<br />

stakeholders.<br />

It is anticipated that the output from UDM may be<br />

used to support and provide evidence in decision<br />

making and the overall safety demonstration <strong>for</strong><br />

aerial dispersion in the Safety Case; particularly relating<br />

to the extent of Emergency Planning Zones. An<br />

aspiration <strong>for</strong> the Advance Modular Reactors (AMRs)<br />

programme in the UK is to reduce these zones to be as<br />

small as possible, so that AMRs can be located closer<br />

to industrial clusters and populated areas. This<br />

would allow <strong>for</strong> the heat generated by the reactor to<br />

be utilised more effectively and in new ways beyond<br />

that of traditional electricity generation.<br />

ENVIRONMENT AND SAFETY 63<br />

Environment and Safety<br />

Dynamic Dispersion Modelling to Enable In<strong>for</strong>med Decision Making in a Modern <strong>Nuclear</strong> Safety Case ı Howard Chapman, Stephen Lawton, Joseph Hargreaves, Robert Gordon, Tim Culmer

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