Home | Introduction | The phosphates file | Current research projects | Bibliography | Contact us
1) Calcium phosphate precipitation chemistry:
a)
heterogeneous nucleation of calcium phosphates and the effects
of inhibitors
b)
precipitation
reactions involving calcite and calcium phosphates
2) The production of waste water sludges for phosphate recovery
5) Feasibility of reuse of recovered phosphate materials in Holland
6) Seeded precipitation of calcium phosphates in wastewaters
7) Investigation of the economic feasibility and environmental efficiency of recovered struvite
8) Metal speciation and nutrient retention by anaerobic digesters
9) Struvite precipitation from sewage liquors, Poland
10) Process optimisation for struvite crystallisation, Treviso, Italy
a) heterogeneous nucleation of calcium phosphates and the effects of inhibitors
PROJECT COMPLETED
Publications:
b)
precipitation
reactions involving calcite
and calcium phosphates
PROJECT COMPLETED
Publications:
Plant, L. & House,
W.A., 2002. Precipitation of calcite in the presence of inorganic
phosphate". Colloids and Surfaces - A - 203, pp. 143-153.
Supervisors: Dr. Elaine
Dick*, Prof. Stephen Allen*, Dr. John Quinn
*School of Chemical Engineering; School of Biology and Biochemistry,
QUESTOR Centre,
The Queen's University of Belfast, N. Ireland
URL: http://questor.qub.ac.uk
Phosphate removal from wastewater is currently achieved by biological and/or chemical treatment methods, producing sludge with an increased phosphate content. These sludges can not at present be used by the phosphate industry as a source of phosphate (P-recovery) if there is significant iron or aluminium content or because P-rich solids are difficult to separate. This project will investigate a novel combination of treatment methods with the aim of producing sludge suitable for P-recovery. The project will involve the operation of a laboratory scale wastewater treatment plant, as well as the detailed examination of microbial physiology and surface chemistry.
Supervisor: Prof Lorenzo Liberti
Institute of Environmental Engineering, Polytechnic University of Bari, 70125 Bari, Italy Tel +39-080-5460368 - Fax +39-080-5460282 - E-mail: liberti@poliba.it
Update and revise the REM-NUT ion exchange process concept to target:
Supervisors: Prof. Bengt Hultmann
Kungl Tekniska Hgskolan Royal Institute of Technology Water Resources Engineering S - 100 44 Stockholm Sweden Email: bgh@aom.kth.se Tel : 46 8 790 6567 Fax : 46 8 790 8689
Project aims are:
Study commissioned by STOWA (Dutch water industry joint research association) and Thermphos (phosphate producer) from HASKONING Ingenieurs en architectenbureau Barbarossastraat 35, Postbus 151 NL-6500 AD Nijmegen Holland Tel 31 24 3284 341 Fax 31 24 360 4737 Email:ws@haskoning.nl
Aims:
Investigators: Dr Dietfried Donnert and co-workers
Karlsruhe Research Centre Forschungszentrum Karlsruhe Technik und Umwelt PO Box 3640 - 76021 Karlsruhe - Germany. Tel : 49 7247 823213 Fax : 49 7247 823478 Email: dietfried.donnert@itc-wgt.fzk.de
Laboratory experimentation of calcium phosphate precipitation from solutions in concentrations comparable to those found in sewage works. Investigation of the effects of different seed crystals and of calcium carbonate/ dissolved inorganic carbon on the calcium phosphate precipitation process.
Papers
Phosphorus removal and recovery by crystallisation
Phosphorus removal combined with active filtration (in german)
P-recovery via crystallisation from waste waters
Study by: Mark GATERELL, Rebecca Gay
Imperial College London Centre Environmental Technology Civil Engineering Building SW7 2BU - London - U.K. Tel. 44 171 594 7459 Fax. 44 171 594 6016/6053 Email: m.gaterell@ic.ac.uk
To investigate the economic feasibility and environmental efficiency of reusing Struvite recovered from wastewater treatment works (WWTW) and other waste streams. This analysis includes an economic evaluation of the recovery process, the identification and investigation of potential re-use options, in particular applications in the fertiliser industry, and the economic and environmental implications of adopting any such options.
EPSRC Grant GR/K96946
INVESTIGATORS: Ms C.M.Carliell, Professor A.D. Wheatley, Dr. M. Ince, Department of Civil and Building Engineering, Loughborough University, Loughborough, Leicestershire LE11 3TU
Summary
Phosphate removal and recovery has and will become important to avoid eutrophication of sensitive waters. The phosphate removed from effluents is concentrated in the sludge. The most common form of sludge treatment in the UK is anaerobic digestion. There was a concern that the solid bound phosphate would be released when subjected to the low redox environment of anaerobic digestion.
Analytical methods were adapted for use in the complex anaerobic environment as a first stage to understanding phosphate mobility. The research reported here developed and modified the standard analytical techniques (Stover and Uhlmann methods) to make them applicable to anaerobic digestion. Changes to the standard analytical techniques are one of the outputs of this research.
Laboratory reactors were used to provide a well controlled environment to study the effect of using chemical flocculents for the precipitation of phosphate compared to biological methods. Calcium and magnesium were also artificially added to simulate their role in scale and struvite formation. The results have shown that increases in soluble phosphorus inhibits digester performance. The chemical equilibrium is normally dominated by the carbonate and sulphide species but this is easily altered by additions of phosphate. Phosphate precipitated with controlled quantities of iron in the laboratory remobilised during anaerobic reduction. Phosphate precipitated with aluminum did not resolubilise.
Field work was carried out on examples of chemical and biological phosphorus removal. The full scale iron dosed sludge did not show any elevated soluble phosphate, in fact the soluble phosphate results were below the detection limit. This was an interesting contrast to the laboratory results where less but controlled amounts of iron were added. Speciation studies showed the phosphate existed as predominantly iron phosphate.
The inference is that iron should be present in a slight excess to avoid re solubilisation on reduction in the digester. There is little chance of scale formation or inhibition because iron competes strongly for the phosphate. In the absence of sufficient ferrous ion then solubilisation or precipitation as struvite and scale is possible. Biological phosphorus removal does carry a greater risk of remobilisation. The formation of struvites in digester ancilaries after biological phosphorus removal has also been reported by others (Rabonowitz and Barnard 1995). In practice our research has shown this will be easy to control by further delicate adjustments to the interlinked inorganic balances. It could be altered by additions of other transition metals for nutrients as well as more iron. Further research on the role of ammonia and alkalinity together with more work on the calcium, magnesium and potassium balances has been suggested to help understand struvite formation.
INVESTIGATORS: Dr Jan Suschka, Technical University of Lodz, Filial Bielsko Biala Email:jsuschka@pb.bielsko.pl
Summary
Testing of different pilot struvite precipitation reactors in sewage
works. Study of parameters affecting the shape of struvite crystals
formed.
INVESTIGATORS: Professor Paolo Battistoni and collaborators, University of Verona, Italy Email: idrotre@mta01.unian.it