People | Locations | Statistics |
---|---|---|
Naji, M. |
| |
Motta, Antonella |
| |
Aletan, Dirar |
| |
Mohamed, Tarek |
| |
Ertürk, Emre |
| |
Taccardi, Nicola |
| |
Kononenko, Denys |
| |
Petrov, R. H. | Madrid |
|
Alshaaer, Mazen | Brussels |
|
Bih, L. |
| |
Casati, R. |
| |
Muller, Hermance |
| |
Kočí, Jan | Prague |
|
Šuljagić, Marija |
| |
Kalteremidou, Kalliopi-Artemi | Brussels |
|
Azam, Siraj |
| |
Ospanova, Alyiya |
| |
Blanpain, Bart |
| |
Ali, M. A. |
| |
Popa, V. |
| |
Rančić, M. |
| |
Ollier, Nadège |
| |
Azevedo, Nuno Monteiro |
| |
Landes, Michael |
| |
Rignanese, Gian-Marco |
|
Boxall, Colin
Lancaster University
in Cooperation with on an Cooperation-Score of 37%
Topics
Publications (26/26 displayed)
- 2022Corrosion Behaviour of AGR Simulated Fuels (SIMFUELs)
- 2019The behaviour of spent nuclear fuel in wet interim storage
- 2019Towards the decontamination of plutonium contaminated bricks
- 2018Mechanisms of fixed contamination of commonly engineered surfaces
- 2017Real time nanogravimetric monitoring of corrosion in radioactive environments
- 2017AGR Cladding Corrosioncitations
- 2016The effect of acetohydroxamic acid on stainless steel corrosion in nitric acidcitations
- 2016Real-Time Nanogravimetric Monitoring of Corrosion in Radioactive Decontamination Systemscitations
- 2016Corrosion of AGR Fuel Pin Steel Under Conditions Relevant to Permanent Disposalcitations
- 2015Corrosion behaviour of AGR SIMFUELScitations
- 2015The effect of SO3-Ph-BTBP on stainless steel corrosion in nitric acidcitations
- 2015Real time nanogravimetric monitoring of corrosion for nuclear decommissioningcitations
- 2013The metallisation of insulating substrates with nano-structured metal films of controllable pore dimensioncitations
- 2013The development of nanoporous metal membranes for analytical separartions
- 2013Nitric acid reduction on 316L stainless steel under conditions representative of reprocessingcitations
- 2013Corrosion behaviour of AGR simulated fuelscitations
- 2013The nanoporous metallisation of polymer membranes through photocatalytically initiated electroless depositioncitations
- 2012Method for formation of porous metal coatings
- 2012Surface Decontamination by Photocatalysis
- 2012The nanoporous metallisation of insulating substrates through Photocatalytically Initiated Electroless Deposition (PIED)
- 2012Semiconductor photocatalysis and metal deposition
- 2012Fixed Contamination on Steel Surfaces: First Use of Quartz Crystal Microgravimetry to Measure Oxide Growth on Process Steels Under Conditions Typical of Nuclear Reprocessingcitations
- 2010Surface decontamination by photocatalysis
- 2009Synthesis of alpha- and beta-FeOOH iron oxide nanoparticles in non-ionic surfactant mediumcitations
- 2006Mesoporous and Nanoparticulate Metal Oxides: Applications in New Photocatalysis
- 2005The applications of photocatalytic waste minimisation in nuclear fuel processingcitations
Places of action
Organizations | Location | People |
---|
document
Surface decontamination by photocatalysis
Abstract
<p>Currently in the nuclear industry, surface contamination in the form of radioactive metal or metal oxide deposits is most commonly removed by chemical decontamination, electrochemical decontamination or physical attrition. Physical attrition techniques are generally used on structural materials (concrete, plaster), with (electro)chemical methods being used to decontaminate metallic or painted surfaces. The most common types of (electro)chemical decontamination are the use of simple mineral acids such as nitric acid or cerium (IV) oxidation (MEDOC). Use of both of these reagents frequently results in the dissolution of a layer of the substrate surface increasing the percentage of secondary waste which leads to burdens on downstream effluent treatment and waste management plants. In this context, both mineral acids and MEDOC can be indiscriminate in the surfaces attacked during deployment, e.g. attacking in transit through a pipe system to the site of contamination resulting in both diminished effect of the decontaminating reagent upon arrival at its target site and an increased secondary waste management requirement. This provides two main requirements for a more ideal decontamination reagent: Improved area specificity and a dissolution power equal to or greater than the previously mentioned current decontaminants.</p><p>Photochemically promoted processes may provide such a decontamination technique. Photochemical reduction of metal ion valence states to aid in heavy metal deposition has already been extensively studied [I], with reductive manipulation also being achieved with uranium and plutonium simulants (Ce) [2]. Importantly photooxidation of a variety of metals, including neptunium [3], has also been achieved. Here we report on the potential application of this technology to metal dissolution.</p>