Dewatering of fine coal — micrographic analysis of filter cake structure

1985 ◽  
Vol 41 (3) ◽  
pp. 239-250 ◽  
Author(s):  
R.M. Kakwani ◽  
H.B. Gala ◽  
S.H. Chiang ◽  
G.E. Klinzing ◽  
J.W. Tierney
Keyword(s):  
1997 ◽  
Vol 52 (7) ◽  
pp. 1151-1162 ◽  
Author(s):  
Florent S. Bourgeois ◽  
Geoffrey J. Lyman

1954 ◽  
Vol 46 (6) ◽  
pp. 1201-1207 ◽  
Author(s):  
Charles E. Silverblatt ◽  
Donald A. Dahlstrom

1984 ◽  
Vol 1 (2) ◽  
pp. 113-117
Author(s):  
R. M. Kakwani ◽  
S. H. Chiang ◽  
G. E. Klinzing
Keyword(s):  

Author(s):  
Vasiliy I. Murko ◽  
Vladimir I. Fedyaev ◽  
Viktor I. Karpenok ◽  
Andrey E. Shanshin ◽  
Amir T. Mukhtarov

The article presents the results of experimental tests of the preparation and combustion of CWF obtained on the basis of finely dispersed waste of coal enrichment (filter cake) of the PP «Energeticheskaya» of the branch «Kaltansky Coal Mine» of the Kuzbassrazrezugol Management Company JSC, at the KuzGTU demonstration semi-industrial stand. The tests carried out have shown that on the basis of the RP filter cake, it is possible to prepare a suspension coal-water fuel with structural-rheological and thermophysical characteristics that ensure efficient combustion of the obtained CWF. For fuel combustion, a boiler with a heating capacity of 0.63 MW with a vortex adiabatic furnace was used. The results obtained confirmed the real possibility of industrial use of the developed technology for the utilization of TDOU in the form of VUT at boiler houses, mini-thermal power plants, state district power stations and other heat-generating installations


1994 ◽  
Vol 11 (1) ◽  
pp. 46-49
Author(s):  
S. M. Khandrika ◽  
J. G. Groppo ◽  
B. K. Parekh
Keyword(s):  

2004 ◽  
Vol 24 (5-6) ◽  
pp. 217-232 ◽  
Author(s):  
D. P. Patil ◽  
B. K. Parekh

2012 ◽  
Vol 41 (9) ◽  
pp. 1191-1196 ◽  
Author(s):  
Sang-Chul Kwon ◽  
Tae-Woog Jeon ◽  
Jeong-Seob Park ◽  
Joon-Soo Kwak ◽  
Tae-Young Kim

2008 ◽  
Vol 3 (1) ◽  
Author(s):  
Karl-Georg Schmelz ◽  
Anja Reipa ◽  
Hartmut Meyer

Emschergenossenschaft and Lippeverband operate 59 wastewater treatment plants which produce approx. 100,000 Mg TS of sewage sludge each year. Using sludge pressure pipelines, about 60 % of this sludge are transported to the central sludge treatment plant in Bottrop. The digested sludges are conditioned using fine coal and polymers and are dewatered using membrane filters. By adding coal, the heating value of the sludge is raised which enables autothermal combustion of the dewatered sludges in fluidised bed furnaces at the central sludge treatment plant. In order to replace coal, a fossil fuel, as conditioning agent, experiments were conducted using alternative materials with high heating values. The addition of shredder fluff agglomerates proved to be particularly successful. Shredder fluff agglomerates are a residue from the recycling of used cars and are generated in a multistage process (e.g. Volkswagen-SiCon Process) by separating the light shredder fraction (plastic components etc.) from the total shredder fluff. The fibrous material is outstandingly suitable for improving the dewaterability and for sufficiently raising the heating value of the dewatered sludge in order to enable autothermal combustion. Since first experiments showed very positive results, a full-scale long-term test-run will take place in 2007.


1987 ◽  
Vol 19 (8) ◽  
pp. 99-105 ◽  
Author(s):  
G. Tesan ◽  
D. Barbosa

The work presented consists of a test procedure applied at a pilot scale using soil as a biological degradation agent. The experiments described were carried out with oily residues considered as wastes difficult to degrade by other means. The tests were applied to filter cake with activated clay containing 40% oil and oily residues from re-refining of lubricants to give white oils and vaseline. The effect of the amount of moisture is evaluated using a mechanical stirrer to improve the interaction between the wastes and microorganisms. The following are also evaluated: nutrient availability; incorporation of micro-organisms into the soil; introduction of chemical fertilizers; and, injections of sludge from effluent treatment plants.


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