GB1572351A - Dewatering of aqueous suspensions of fine particulate solids - Google Patents
Dewatering of aqueous suspensions of fine particulate solids Download PDFInfo
- Publication number
- GB1572351A GB1572351A GB21216/76A GB2121676A GB1572351A GB 1572351 A GB1572351 A GB 1572351A GB 21216/76 A GB21216/76 A GB 21216/76A GB 2121676 A GB2121676 A GB 2121676A GB 1572351 A GB1572351 A GB 1572351A
- Authority
- GB
- United Kingdom
- Prior art keywords
- weight
- aqueous suspension
- suspension
- water
- aluminium
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000007900 aqueous suspension Substances 0.000 title claims description 38
- 239000007787 solid Substances 0.000 title claims description 32
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 37
- 239000000725 suspension Substances 0.000 claims description 31
- 239000004411 aluminium Substances 0.000 claims description 28
- 229910052782 aluminium Inorganic materials 0.000 claims description 28
- 229920000642 polymer Polymers 0.000 claims description 28
- 125000002887 hydroxy group Chemical group [H]O* 0.000 claims description 27
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 26
- 230000035699 permeability Effects 0.000 claims description 24
- 239000002245 particle Substances 0.000 claims description 23
- 238000000034 method Methods 0.000 claims description 20
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 19
- 229910052751 metal Inorganic materials 0.000 claims description 19
- 239000002184 metal Substances 0.000 claims description 19
- 239000011707 mineral Substances 0.000 claims description 19
- 239000010427 ball clay Substances 0.000 claims description 16
- 238000002474 experimental method Methods 0.000 claims description 16
- 230000000717 retained effect Effects 0.000 claims description 16
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 14
- 239000012065 filter cake Substances 0.000 claims description 14
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 12
- 229910019142 PO4 Inorganic materials 0.000 claims description 12
- 239000010452 phosphate Substances 0.000 claims description 12
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims description 12
- 238000011065 in-situ storage Methods 0.000 claims description 8
- 150000003839 salts Chemical class 0.000 claims description 7
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 7
- 239000001164 aluminium sulphate Substances 0.000 claims description 6
- 235000011128 aluminium sulphate Nutrition 0.000 claims description 6
- BUACSMWVFUNQET-UHFFFAOYSA-H dialuminum;trisulfate;hydrate Chemical compound O.[Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O BUACSMWVFUNQET-UHFFFAOYSA-H 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 6
- 229910052742 iron Inorganic materials 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 6
- 238000011085 pressure filtration Methods 0.000 claims description 6
- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 0.000 claims description 5
- 229910052901 montmorillonite Inorganic materials 0.000 claims description 5
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 claims description 3
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims description 3
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 3
- 229910052804 chromium Inorganic materials 0.000 claims description 3
- 239000011651 chromium Substances 0.000 claims description 3
- 239000004927 clay Substances 0.000 claims description 3
- 239000011777 magnesium Substances 0.000 claims description 3
- 229910052749 magnesium Inorganic materials 0.000 claims description 3
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 239000011701 zinc Substances 0.000 claims description 3
- 229910052725 zinc Inorganic materials 0.000 claims description 3
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 claims description 2
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims description 2
- 229910052586 apatite Inorganic materials 0.000 claims description 2
- 239000010459 dolomite Substances 0.000 claims description 2
- 229910000514 dolomite Inorganic materials 0.000 claims description 2
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 claims description 2
- VSIIXMUUUJUKCM-UHFFFAOYSA-D pentacalcium;fluoride;triphosphate Chemical compound [F-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O VSIIXMUUUJUKCM-UHFFFAOYSA-D 0.000 claims description 2
- 239000010453 quartz Substances 0.000 claims description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 2
- 239000000706 filtrate Substances 0.000 description 8
- -1 fuller's earth Chemical compound 0.000 description 5
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 229910000275 saponite Inorganic materials 0.000 description 3
- 239000001117 sulphuric acid Substances 0.000 description 3
- 235000011149 sulphuric acid Nutrition 0.000 description 3
- HPTYUNKZVDYXLP-UHFFFAOYSA-N aluminum;trihydroxy(trihydroxysilyloxy)silane;hydrate Chemical compound O.[Al].[Al].O[Si](O)(O)O[Si](O)(O)O HPTYUNKZVDYXLP-UHFFFAOYSA-N 0.000 description 2
- 239000000440 bentonite Substances 0.000 description 2
- 229910000278 bentonite Inorganic materials 0.000 description 2
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 2
- 239000002734 clay mineral Substances 0.000 description 2
- 229910001649 dickite Inorganic materials 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 229910052621 halloysite Inorganic materials 0.000 description 2
- 229910052622 kaolinite Inorganic materials 0.000 description 2
- CYPPCCJJKNISFK-UHFFFAOYSA-J kaolinite Chemical compound [OH-].[OH-].[OH-].[OH-].[Al+3].[Al+3].[O-][Si](=O)O[Si]([O-])=O CYPPCCJJKNISFK-UHFFFAOYSA-J 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229910000269 smectite group Inorganic materials 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical class [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 description 1
- 229910021502 aluminium hydroxide Inorganic materials 0.000 description 1
- ANBBXQWFNXMHLD-UHFFFAOYSA-N aluminum;sodium;oxygen(2-) Chemical compound [O-2].[O-2].[Na+].[Al+3] ANBBXQWFNXMHLD-UHFFFAOYSA-N 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 229910003460 diamond Inorganic materials 0.000 description 1
- 239000010432 diamond Substances 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 230000005294 ferromagnetic effect Effects 0.000 description 1
- 238000007885 magnetic separation Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 230000005298 paramagnetic effect Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 229910001388 sodium aluminate Inorganic materials 0.000 description 1
- HVTHJRMZXBWFNE-UHFFFAOYSA-J sodium zincate Chemical compound [OH-].[OH-].[OH-].[OH-].[Na+].[Na+].[Zn+2] HVTHJRMZXBWFNE-UHFFFAOYSA-J 0.000 description 1
- 229910021653 sulphate ion Inorganic materials 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/20—Treatment or purification of solutions, e.g. obtained by leaching
- C22B3/44—Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Geology (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Manufacturing & Machinery (AREA)
- General Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Geochemistry & Mineralogy (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Filtration Of Liquid (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Water Treatment By Sorption (AREA)
Description
(54) IMPROVEMENTS IN OR RELATING TO THE DEWATERING OF AQUE
OUS SUSPENSIONS OF FINE PARTICULATE SOLIDS
(71) We, ENGLISH CLAYS LOVERING POCHIN & COMPANY LIMITED, a
British company, of John Keay House, St. Austell, Cornwall, PL25 4DJ, do hereby declare the invention, for which we pray that a patent may be granted to us, and the method by which it is to be performed, to be particularly described in and by the following statement:
This invention relates to the dewatering of aqueous suspensions of fine particulate solids, for example a mineral by pressure filtration.
Dry methods of mineral beneficiation are generally only applicable to minerals comprising particles which have a diameter predominantly larger than about 10 microns (10 tom).
When the particle size of the mineral is substantially smaller than about 10 ,um, it becomes necessary to beneficiate the mineral in suspension in a liquid, generally water, in order to achieve a sharp separation of impurities or gangue from the desired product. Unfortunately, if the mineral particles are very fine it is difficult to dewater them mechanically by conventional means, i.e. by filtration or gravitational or centrifugal sedimentation, because the particles pack together to form a bed or cake which is very impermeable to the suspending liquid. Examples of materials which behave in this way are very fine clays of the kandite group, e.g. kaolinite, dickite, nacrite or halloysite, or of the smectite group, e.g. montmorillonite, fuller's earth, bentonite or saponite, and mineral residues which contain substantial proportions of these clays.
According to the present invention there is provided a method of mechanically dewatering an aqueous suspension of a fine particulate solid containing at least 40% by weight of particles having an equivalent spherical diameter smaller than 1 micron by pressure filtration at a pressure greater than 250 pounds per square inch which method comprises mixing with the aqueous suspension of the fine particulate solid prior to the dewatering thereof a minor amount of a water-soluble salt of a di- or multi-valent metal, adjusting the pH of the aqueous suspension to a value, in the range 3.5 to 9.0, such that there is formed in situ in the aqueous suspension a precipitate of a substantially water-insoluble hydroxy polymer of the di- or multivalent metal, and maintaining the pH of the aqueous suspension at a value in said range of from 3.5 to 9.0 so that the precipitate of said hydroxy polymer of the di- or multivalent metal does not dissolve in the water of said aqueous suspension ; and thereafter mechanically dewatering said aqueous suspension by pressure filtration at a pressure greater than 250 pounds per square inch.
Information about hydroxy polymers of di- or multivalent metals is given in the following literature references:
(i) "Fixation of Phosphate by Aluminium and Iron in Acidic Soils" by Pa Ho Hsu, Soil
Science, Vol. 99, No. 6, pages 398-402 (1965);
(ii) "Formation of X-ray amorphous and Crystalline Aluminium Hydroxides" by Pa Ho
Hsu and T.R. Bates, Mineralogical Magazine, Vol. 33, pages 749-68 (1964); and
iii) British Patent Specification No. 1,481,118.
The inorganic hydroxy polymer is precipitated in situ in the aqueous suspension, i.e in the presence of the fine particulate solid, by adding thereto a water-soluble salt of the di- or multi-valent metal and adjusting the pH of the aqueous suspension to a value at which precipitation of the hydroxy polymer occurs. The water-soluble salt of the element may be a salt in which the element is the cation, for example the sulphate, nitrate or chloride of the element, or a salt in which the element is present in the anion, for example sodium aluminate or sodium zincate.
In one embodiment of the present invention, a positively charged inorganic hydroxy polymer of aluminium, iron, magnesium, chromium, manganese, colbalt or zinc is formed in situ in an aqueous suspension of a fine mineral in a quantity such that there is present in the aqueous suspension from 0.5 to 30.0 mg. of the metal per gram of the fine mineral, calculated on a dry weight basis, and under conditions such that the pH of the aqueous suspension containing the fine mineral and the inorganic hydroxy polymer is at a value such that the inorganic hydroxy polymer does not dissolve in the water of said aqueous suspension.
The amount of the inorganic hydroxy polymer precipitated in situ in the suspension of the fine particulate solid is preferably such that there is present in the suspension a quantity of the metal in the range of from 0.1 to 15.0 mg of metal per gram of the fine particulate solid.
The aqueous suspension containing the fine particulate solid and the hydroxy polymer is dewatered by filtration at a pressure greater than 250 pounds per square inch.
When the mineral is the desired product the di- or multi-valent metal is preferably aluminium, as hydroxy polymers of aluminium introduce no undesirable impurities. When a hydroxy polymer of aluminium is employed the average ratio of hydroxide ions to aluminium ions is preferably in the range of from 0.5 to 2.8 and the pH at which the hydroxy polymer is precipitated in the aqueous suspension of the particulate solid is preferably in the range from 5 to 7. When however, the mineral is a waste material which it is required to dewater so that it can be disposed of and the water in which it was suspended can be recovered, the di- or multi-valent metal may be iron, magnesium, chromium, manganese, cobalt, zinc or aluminium.
The fine mineral will frequently be or comprise a substantial proportion of a clay mineral of the kandite group, e.g. kaolinite, nacrite, dickite or halloysite, or a clay mineral of the smectite group, e.g montmorillonite, fuller's earth, bentonite or saponite. The method of the invention is especially suitable for treating very fine mineral raw materials, such as ball clay, and for treating fine waste products of mineral beneficiation processes such as Florida pebble phosphate slimes (which containapatite and montmorillonite) and kimberlite slimes from the diamond mines of the Kimberley area (which consist predominantly of saponite).
Such fine minerals will generally have a particle size distribution such that at least 60% by weight of the particles have an equivalent spherical diameter smaller than 1 micron.
The follow experiments demonstrate the improvement in the permeability of a filter cake of a fine particulate solid which is achieved when a hydroxy polymer of a di- or multivalent metal is precipitated in situ in an aqueous suspension of the fine particulate solid.
Experiment clay having 1 A Dorset ball clay having a particle size distribution such that 4% by weight consisted of particles having an equivalent spherical diameter larger than 5m, m, 79% by weight consisted of particles having an equivalent spherical diameter smaller than 1calm and 62% by weight consisted of particles having an equivalent spherical diameter smaller than 0.5clam, was mixed with water to form a suspension containing 50% by weight of dry ball clay. Sufficient sodium hydroxide was added to the suspension to raise its pH to 8.5. The suspension was subjected to agitation in a high speed mixer for a time sufficient to dissipate in the suspension about 50KJ of energy per kg. of dry clay.
The suspension was then diluted with water to 20% by weight of dry ball clay, screened through a No. 300 mesh B.S. sieve (nominal aperture 53clam) and subjected to a magnetic separation step to remove ferromagnetic and paramagnetic impurities.
A portion of the screened and magnetically beneficiated ball clay suspension was then treated with sulphuric acid to reduce the pH to 4.0 and the permeability to water of a filter cake formed from the ball clay suspension at a pressure differential of 100 psi (689 kNm-2) was measured by the following method:
The apparatus used consisted of a cylindrical vessel in which a closely fitting piston could slide, the ends of the cylindrical vessel being closed by screw-threaded end caps. In one end cap there was provided an outlet conduit for filtrate the opening to which conduit was covered by a piece of wire gauze surmounted by a piece of filter cloth which together acted
as a filter medium on which a filter cake could be built up. The other end cap was provided with a conduit through which hydraulic fluid could be supplied at an elevated pressure. In operation, the end cap comprising the filter medium was unscrewed and a sample of the suspension to be tested was introduced into the cavity between the upper end of the piston
and the filter medium. Hydraulic fluid at the required pressure was then introduced into the cavity between the other end of the piston and the other end cap, pressure being thereby
applied to the suspension. Filtrate expressed through the filter medium was collected in a graduated cylinder and the volume of filtrate collected aften given intervals of time was
observed. A graph was then plotted of t/V against V, where V is the volume of filtrate
collected after time t. A straight line was obtained and the slope, m, was estimated.
The permeability, p, was calculated from the expression p= v
2A2 AP.m where AP is the pressure drop across the filter medium and the cake;
A is the surface area of the filter medium perpendicular to the direction of flow of filtrate, and v is the volume of cake deposited per unit volume of filtrate and is given by the expression
v = ds - df dc - ds where ds is the specific gravity of the feed suspension,
df is the specific gravity of the filtrate and dc is the specific gravity of the filter cake.
The permeability is expressed as cubic inches of filtrate per hour passing through a cube of filter cake of side one inch under a pressure differential of one pound per square inch()psi).
Further portions of the screened and magnetically beneficiated ball clays suspension were then subjected to treatment with different amounts of an aluminium hydroxy polymer by reducing the pH to 4.0 with dilute sulphuric acid, adding the amount of aluminium sulphate which would provide the desired dose of aluminium per unit weight of dry ball clay and, finally, adjusting the pH to 6.8 with sodium carbonate to precipitate a hydroxy polymer of aluminium.
The permeability of the filter cake at a pressure differential of 100 psi was measured in each case as described above and the percentage by weight of water remaining in the cake was also measured. The results obtained are set forth in Table 1 below.
TABLE 1
Aluminium dose
(mg Al per g. of Permeability % by wt. of water
dry ball clay) x 10-4 retained in cake
0 3.5 37.6
2 10.8 40.8
4 32.3 45.8
8 68.9 48.3
16 114.5 51.5
It will be appreciated that, although the amount of water retained in the cake increases with increasing aluminium dose, the low water content corresponding to zero aluminium dose could not be achieved commercially because filtration would be prohibitively slow on account of the low filter cake permeability.
The portion of the suspension which had been treated with 4 mg of Al per g. of dry ball clay exhibited a good improvement in permeability which rendered it easily dewatered by filtration at high pressures and at the same time the water content of the cake was not increased to an undesirable level and the dose of aluminium was not excessive.
Experiment 2
Experiment 1 was repeated except that the portions of the screened and magnetically beneficiated ball clay suspension were not treated with dilute sulphuric acid to reduce the pH from 7.5 to 4.0 before addition of aluminium sulphate but the aluminium sulphate was added to the suspension at its pH of about 7.5. The addition of the aluminium sulphate itself reduced the pH to about 3.5 and the pH was of the suspension then adjusted to 6.8 with sodium carbonate to precipitate a hydroxy polymer of aluminium.
The permeability of the filter cake at a pressure differential of 100 psi and the percentage by weight of water retained in the cake were measured in each case and the results are set forth in Table II below.
TABLE II
Aluminium dose
(mg Al per g. of Permeability % by weight of water
dry ball clay x 10-4 retained in cake
0 3.5 37.6
2 16.8 44.8
4 36.8 44.9
8 58.2 49.8
Experiment 3
Further portions of the same suspension of screened and magnetically beneficiated ball clay as was used in Experiments 1 and 2 were treated at their pH of 7.5 with the same dose of aluminium, namely 8 mg. of Al per g. of dry ball clay, but subsequently different amounts of sodium carbonate were added to give different values of the final pH and to give different hydroxy polymers of aluminium.
The permeability and water content of the cake after filtration at the different pH values were measured by the method described in Experiment 1 and the results are set forth in
Table III below.
TABLE III
pH Permeability x 10-4 %wit. of water retained
in cake
3.5 12.7 41.4
4.0 52.8 44.8
5.0 69.9 49.5
6.0 62.4 50.7
6.8 63.6 49.1
8.0 36.2 48.6
9.0 23.7 47.4
It can be seen that when the ball clays are treated with a hydroxy polymer of aluminium, it is important that the final pH is in the range from 4 to 8 and preferably is in the range from 5 to7.
Experiment 4
A sample of Florida pebble phosphate slime had a particle size distribution such that substantially all of the particles were smaller than 100 cam (i.e. passed a No. 150 mesh B.S.
Sieve), 27% by weight consisted of particles having an equivalent spherical diameter larger than slum, 60% by weight consisted of particles having an equivalent spherical diameter smaller than 1,um, and 51% by weight consisted of particles having an equivalent spherical diameter smaller than 0.5,us. The slime consisted of about 30%by weight of apatite, about 60% by weight of montmorillonite, about 5% by weight of quartz and about 5% by weight of dolomite.
The phosphate slime was mixed with water to form a suspension containing about 10% by weight of dry solids and the suspension was divided into three portions. The first portion was tested to determine the permeability of the filter cake under a pressure differential of 100 psi according to the method described in Experiment 1, and the percentage by weight of water retained in the cake was measured. The second and third portions were treated with aluminium sulphate solutions in amounts such that there were added to the phosphate slime 5 mg and 15 mg of aluminium respectively per gram of dry solids. The pH of each portion of treated suspension was then adjusted to 6.0 with sodium carbonate to precipitate a hydroxy polymer of aluminium, and the permeability and percentage by weight of water retained by the filter cakes were then measured. The results obtained are set forth in Table
IV below.
TABLE IV
Aluminium dose (mg Al per Permeability % by weight
g. of dry solids) x 10-4 water retained
in cake
0 1.2 55.1
5 23.2 58.2
15 25.8 59.4
Experiment 5
A further sample of the same Florida pebble phosphate slime as was used in Experiment 4 was mixed with water to form a suspension containing about 10% by weight of dry solids.
The suspension was treated with ferric chloride solution in an amount such that there were added to the phosphate slime 10 mg of iron per gram of dry solids. The pH of the treated suspension was then adjusted to 4.5 with sodium carbonate to precipitate a hydroxy polymer of ferric iron, and the permeability and percentage by weight of water retained by the filter cake were then measured. The permeability was 15.4 x 10-4 cubic inches of water per hour per one inch cube of cake per psi and the percentage by weight of water retained in the cake was 58.0.
WHAT WE CLAIM IS:
1. A method of mechanically dewatering an aqueous suspension of a fine particulate solid containing at least 40% by weight of particles having an equivalent spherical diameter smaller than 1 micron by pressure filtration at a pressure greater than 250 pounds per square inch, which method comprises mixing with the aqueous suspension of the fine particulate solid prior to the dewatering thereof a minor amount of a water soluble salt of a di- or multi-valent metal, adjusting the pH of the aqueous suspension to a value, in the range 3.5 to 9.0, such that there is formed in situ in the aqueous suspension a precipitate of a substantially water-insoluble hydroxy polymer of the di- or multi-valent metal, and maintaining the pH of the aqueous suspension at a value in said range of from 3.5 to 9.0 so that
**WARNING** end of DESC field may overlap start of CLMS **.
Claims (1)
- **WARNING** start of CLMS field may overlap end of DESC **.The permeability and water content of the cake after filtration at the different pH values were measured by the method described in Experiment 1 and the results are set forth in Table III below.TABLE III pH Permeability x 10-4 %wit. of water retained in cake3.5 12.7 41.44.0 52.8 44.85.0 69.9 49.56.0 62.4 50.76.8 63.6 49.18.0 36.2 48.69.0 23.7 47.4 It can be seen that when the ball clays are treated with a hydroxy polymer of aluminium, it is important that the final pH is in the range from 4 to 8 and preferably is in the range from 5 to7.Experiment 4 A sample of Florida pebble phosphate slime had a particle size distribution such that substantially all of the particles were smaller than 100 cam (i.e. passed a No. 150 mesh B.S.Sieve), 27% by weight consisted of particles having an equivalent spherical diameter larger than slum, 60% by weight consisted of particles having an equivalent spherical diameter smaller than 1,um, and 51% by weight consisted of particles having an equivalent spherical diameter smaller than 0.5,us. The slime consisted of about 30%by weight of apatite, about 60% by weight of montmorillonite, about 5% by weight of quartz and about 5% by weight of dolomite.The phosphate slime was mixed with water to form a suspension containing about 10% by weight of dry solids and the suspension was divided into three portions. The first portion was tested to determine the permeability of the filter cake under a pressure differential of 100 psi according to the method described in Experiment 1, and the percentage by weight of water retained in the cake was measured. The second and third portions were treated with aluminium sulphate solutions in amounts such that there were added to the phosphate slime 5 mg and 15 mg of aluminium respectively per gram of dry solids. The pH of each portion of treated suspension was then adjusted to 6.0 with sodium carbonate to precipitate a hydroxy polymer of aluminium, and the permeability and percentage by weight of water retained by the filter cakes were then measured. The results obtained are set forth in Table IV below.TABLE IV Aluminium dose (mg Al per Permeability % by weight g. of dry solids) x 10-4 water retained in cake 0 1.2 55.1 5 23.2 58.2 15 25.8 59.4 Experiment 5 A further sample of the same Florida pebble phosphate slime as was used in Experiment 4 was mixed with water to form a suspension containing about 10% by weight of dry solids.The suspension was treated with ferric chloride solution in an amount such that there were added to the phosphate slime 10 mg of iron per gram of dry solids. The pH of the treated suspension was then adjusted to 4.5 with sodium carbonate to precipitate a hydroxy polymer of ferric iron, and the permeability and percentage by weight of water retained by the filter cake were then measured. The permeability was 15.4 x 10-4 cubic inches of water per hour per one inch cube of cake per psi and the percentage by weight of water retained in the cake was 58.0.WHAT WE CLAIM IS:1. A method of mechanically dewatering an aqueous suspension of a fine particulate solid containing at least 40% by weight of particles having an equivalent spherical diameter smaller than 1 micron by pressure filtration at a pressure greater than 250 pounds per square inch, which method comprises mixing with the aqueous suspension of the fine particulate solid prior to the dewatering thereof a minor amount of a water soluble salt of a di- or multi-valent metal, adjusting the pH of the aqueous suspension to a value, in the range 3.5 to 9.0, such that there is formed in situ in the aqueous suspension a precipitate of a substantially water-insoluble hydroxy polymer of the di- or multi-valent metal, and maintaining the pH of the aqueous suspension at a value in said range of from 3.5 to 9.0 so thatthe precipitate of said hydroxy polymer of the di- or multi-valent metal does not dissolve in the water of said aqueous suspension; and thereafter mechanically dewatering said aqueous suspension by pressure filtration at a pressure greater than 250 pounds per square inch.2. A method of dewatering an aqueous suspension of a fine particulate solid according to claim 1, wherein said fine particulate solid is a mineral, wherein said di- or multi-valent metal is aluminium, iron, magnesium, chromium, manganese, colbalt or zinc, and wherein the quantity of said precipitate of the hydroxy polymer which is formed in situ in said aqueous suspension is such that there is present in the aqueous suspension from 0.5 to 30.0 mg. of the metal per gram of the mineral, calculated on a dry weight basis.3. A method of dewatering an aqueous suspension of a fine particulate solid according to claim 2, wherein said mineral contains a substantial proportion of a clay.4. A method of dewatering an aqueous suspension of a fine particulate solid according to claim 3, wherein said multi-valent metal is aluminium and wherein the pH of the aqueous suspension is adjusted to a value in the range of from 5 to 7.5. A method of dewatering an aqueous suspension of a fine particulate solid according to claim 1 and substantially as hereinbefore described.6. A fine particulate solid whenever obtained by a method according to any one of the preceding claims.
Priority Applications (7)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB21216/76A GB1572351A (en) | 1976-05-21 | 1976-05-21 | Dewatering of aqueous suspensions of fine particulate solids |
| ZA00772802A ZA772802B (en) | 1976-05-21 | 1977-05-10 | Dewatering of fine particulate solids |
| FR7715280A FR2351689A1 (en) | 1976-05-21 | 1977-05-18 | IMPROVED PROCESS FOR THE REMOVAL OF WATER FROM SOLIDS IN FINE PARTICLES |
| AU25246/77A AU507341B2 (en) | 1976-05-21 | 1977-05-18 | Dewatering of fine particulate solids |
| ES458966A ES458966A1 (en) | 1976-05-21 | 1977-05-19 | Dewatering of aqueous suspensions of fine particulate solids |
| DE19772722913 DE2722913A1 (en) | 1976-05-21 | 1977-05-20 | PROCESS FOR DEWATERING FINE-GRAY SOLIDS |
| JP52057819A JPS6013726B2 (en) | 1976-05-21 | 1977-05-20 | Dehydration method for aqueous suspensions of fine-grained solids |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB21216/76A GB1572351A (en) | 1976-05-21 | 1976-05-21 | Dewatering of aqueous suspensions of fine particulate solids |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| GB1572351A true GB1572351A (en) | 1980-07-30 |
Family
ID=10159141
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| GB21216/76A Expired GB1572351A (en) | 1976-05-21 | 1976-05-21 | Dewatering of aqueous suspensions of fine particulate solids |
Country Status (7)
| Country | Link |
|---|---|
| JP (1) | JPS6013726B2 (en) |
| AU (1) | AU507341B2 (en) |
| DE (1) | DE2722913A1 (en) |
| ES (1) | ES458966A1 (en) |
| FR (1) | FR2351689A1 (en) |
| GB (1) | GB1572351A (en) |
| ZA (1) | ZA772802B (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0070631A1 (en) * | 1981-07-16 | 1983-01-26 | Ecc International Limited | Stabilisation of photochromic compounds, and the use of stabilised photochromic compounds |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR1379343A (en) * | 1964-01-02 | 1964-11-20 | Beteiligungs & Patentverw Gmbh | Fine sludge dewatering process |
| DE1642850A1 (en) * | 1967-05-16 | 1971-03-11 | Metallgesellschaft Ag | Process for dewatering organic sludge by centrifugation |
| DE1965734A1 (en) * | 1969-12-31 | 1971-07-08 | Degussa | Peat as filtering aid in clearing sludge - dehydration |
| NL7214504A (en) * | 1972-10-26 | 1974-05-01 | ||
| GB1428846A (en) * | 1973-03-30 | 1976-03-17 | English Clays Lovering Pochin | Separation of fine solids and liquids |
-
1976
- 1976-05-21 GB GB21216/76A patent/GB1572351A/en not_active Expired
-
1977
- 1977-05-10 ZA ZA00772802A patent/ZA772802B/en unknown
- 1977-05-18 FR FR7715280A patent/FR2351689A1/en not_active Withdrawn
- 1977-05-18 AU AU25246/77A patent/AU507341B2/en not_active Expired
- 1977-05-19 ES ES458966A patent/ES458966A1/en not_active Expired
- 1977-05-20 DE DE19772722913 patent/DE2722913A1/en not_active Withdrawn
- 1977-05-20 JP JP52057819A patent/JPS6013726B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0070631A1 (en) * | 1981-07-16 | 1983-01-26 | Ecc International Limited | Stabilisation of photochromic compounds, and the use of stabilised photochromic compounds |
Also Published As
| Publication number | Publication date |
|---|---|
| ES458966A1 (en) | 1978-02-16 |
| AU507341B2 (en) | 1980-02-14 |
| ZA772802B (en) | 1978-04-26 |
| JPS6013726B2 (en) | 1985-04-09 |
| DE2722913A1 (en) | 1977-12-01 |
| AU2524677A (en) | 1978-11-23 |
| JPS537588A (en) | 1978-01-24 |
| FR2351689A1 (en) | 1977-12-16 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US3020231A (en) | Coagulation | |
| Feng et al. | Removal of heavy metal ions by carrier magnetic separation of adsorptive particulates | |
| KR100788119B1 (en) | Granular Contact and Adsorbent | |
| EP1328476B1 (en) | Contact and adsorber granulates | |
| DE2600926A1 (en) | METHOD OF DRAINING OF COLLOIDAL MINERAL AND MICROBIAL MUDDLE WASTE | |
| US5307938A (en) | Treatment of iron ore to increase recovery through the use of low molecular weight polyacrylate dispersants | |
| US6383282B1 (en) | Pseudophasic extraction method for the separation of ultra-fine minerals | |
| KR20210036383A (en) | Removal of heavy metals using minerals functionalized as adsorption enhancers | |
| CH660587A5 (en) | Composition for the treatment of contaminated waste waters, process for the production of the composition and waste-water purification process | |
| Kitchener | Flocculation in mineral processing | |
| US4225425A (en) | Method for separating metallic minerals utilizing magnetic seeding | |
| O'Gorman et al. | The flocculation and de-watering of kimberlite clay slimes | |
| GB1583881A (en) | Water clarification | |
| US2394083A (en) | Surface active agents | |
| US2862880A (en) | Method of clarifying water by hydrophobic polyamines | |
| US4219408A (en) | Magnetic separation of minerals utilizing magnetic particulates | |
| Hogg et al. | Agglomerate structure in flocculated suspensions and its effect on sedimentation and dewatering | |
| US5910253A (en) | Removal of metal ions from aqueous solution | |
| DE2410394A1 (en) | PROCESS FOR DRAINING AN AQUATIC SLUDGE OF DISPERSED, FINELY CRUSHED SOLIDS | |
| CN109592759A (en) | A kind of board wastewater treatment agent and its preparation, application method | |
| Bagster et al. | Studies in the selective flocculation of hematite from gangue using high molecular weight polymers. Part 1: Chemical factors | |
| GB1572351A (en) | Dewatering of aqueous suspensions of fine particulate solids | |
| US4051027A (en) | Settling clay-containing slimes | |
| Dawei et al. | Hydrophobic agglomeration and spherical agglomeration of wolframite fines | |
| Schiller et al. | Mineral processing water treatment using magnesium oxide |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PS | Patent sealed | ||
| PCNP | Patent ceased through non-payment of renewal fee |