FLOTATION AND WASHRNG OF SLWY
GELAHHOUS FRECEPITATES OF OXYGENATED
METALS
Thesis for the Dogm 91‘ M. S.
MWHFGAN STATE UNWEafiTY
Donald Rober? parker
1958
“4rfi‘5
This is to certify that the
thesis entitled
Flotation and Washing of Slimy Gelatinous
Precipitates of Oxygenated Metals
presented by
Donald Robert Parker
has been accepted towards fulfillment
of the requirements for
Master of Science degree in Chemical Engineering
0-169
FLOTATION AND WASHING OF SLINY GELATINOUS PRECIPITATES
OF OXYGENATED METALS
by
DONALD ROBERT PARKER
AN ABSTRACT
Submitted to the School for Advanced Graduate Studies of
Michigan State University of Agriculture and
Applied Science in partial fulfillment of
the requirements for the degree of
MASTER OF SCIENCE
Department of Chemical Engineering
1958
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Approved: <:///' éVV~L/‘f '"M )
ABSTRACT
This is a report of an investigation to examine the
feasibility of using flotation as a method for washing slimy
gelatinous precipitates. The precipitates studied were the
hydroxides of magnesium, nickel, copper, cadmium, and zinc,
and the hydrous oxides of aluminum, iron, manganese, chromium,
and cobalt. Particular emphasis was placed upon the flota-
tion and washing preperties of gelatinous magnesium and
aluminum.
Flotation of the precipitates was accomplished in a
machine designed to cause flotation by release of dissolved
air. The machine was similar in principle to the Sveen-
Pedersen Saveall used in the paper industry for white water
clarification.
Oleic acid was found to be effective as a collector
for all the precipitates studied with the exception of cupric
hydroxide. Cupric hydroxide was floated using eosin red dye
as an activator and emulsified light machine oil as a
collector.
Data are presented to show the relative efficiency of
several organic acids as collector reagents. The influence
of temperature upon collector efficiency and adherence
during washing was also studied. Results indicate that at
temperatures exceeding 120° F the gelatinous precipitates of
aluminum and magnesium may be floated and washed three times
with no appreciable loss of precipitate.
FLOTATION AND WASHING OF SLIMY GELATINOUS PRECIPITATES
OF OXYGENATED METALS
by
DONALD ROBERT PARKER
A THESIS
Submitted to the School for Advanced Graduate Studies of
Michigan State University of Agriculture and
Applied Science in partial fulfillment of
the requirements for the degree of
MASTER OF SCIENCE
Department of Chemical Engineering
1958
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ACECII OU’.’LEDGEF$EIIT
The author wishes to eXpress his appreciation to Dr.
Clyde C. Dewitt for he guidance and encouragement which he
gave throughout the course of this investigation.
Thanks are also due to the Dura-Metallic Corporation of
Kalamazoo, Michigan, for their generous donation of a Dura-
Scal air tight bearing for this work.
TABLE OF CONTENTS
CHAPTER PAGE
ACKNOWLEDGEMENT . . . . . . . . . . . . . . . . . . ii
I. III'I‘RODUCTION O O O O O C O O C I O O O C O O C l
Flotation Applied to Problem of Washing Slimy
PPeCipitates O O O O O O O O O O O O O O 0
Scope of the Investigation . . . . . . . . .
O‘UIF'
II. EXPERIMENTAL EQUIPMENT . . . . . . . . . . . .
III. PRELIMINARY EXPERIMENTAL WORK . . . . . . . . 11
Survey of Metallic Hydroxides and Hydrated
0x1des O O O O O O C I O O C O I O O O O O 11
Flotation EXperiments with Digested Bauxite 11
Experimental Variables . . . . . . . . . . . 13
IV . 12R OCEDURE O O O O O O C O O O O O O O C O O C 15
Usual procedure Followed in Making Individual
Trial Flotation Tests on Gelatinous Aluminum
and Magnesium . . . . . . . . . . . . . . 15
v. EXPERIMENTAL SECTION . . . . . . . . . . . . . 18
‘Reagents Tested as Collectors . . . . . . . 18
Water Emulsions of Oleic and Linoleic Acid . 18
Turbidity Determination to Measure Flotation
Results 0 O O O O O O O O O O O I O O C . 2O
Flotation of Magnesium Hydroxide at 1150 F
Using an Oleic Acid Emulsion . . . . . . . 28
Effect of Temperature on Efficiency of
COlleCtor O O O O O O O O O O O O O O O O 39
Repeated Flotation and Washing of the Aluminum
Oxide and Magnesium Hydroxide Precipitates ho
VI. DISUCSSION . . . . . . . . . . . . . . . . . SS
Bubble Attachment . . . . . . . . . . . . . 55
iii
CHAPTER PAC“
Relative Efficiency of Some Organic Acids as ’
Collectors . . . . . . . . . . . . . . . . . 56
Frothing . . . . . . . . . . . . . . . . . . . 60
pH as a Variable . . . . . . . . . . . . . . . 62
Air Flow Through the Chamber . . . . . . . . . 63
Air Pressure in the Chamber . . . . . . . . . 63
Release of Air Pressure . . . . . . . . . . . 6S
Agitation . . . . . . . . . . . . . . . . . . 6S
Washing the Precipitates . . . . . . . . . . . 66
Hardness of Water and Its Effect upon Results 67
VII. CONCLUSIONS . . . . . . . . . . . . . e e . e 0 7O
BIBLIOGRAPIIY O O O O O O O O O O O O O 0 O O O O O O O 71
iv
FIGURE
1.
ll.
12.
15.
16.
17.
18.
19h-
20.
21.
LIST OF FIGURES
PAGE
The flotation machine and auxilary equipment . . 7
The flotation machine and auxilary equipment . . 7
Close-up of lower section of flotation machine . 8
Sketch of the air pressure relief valve . . . . 9
Transmission curve for gelatinous aluminum . . . 2h
Transmission curve for gelatinous magnesium . . 26
Mg(OH)2 flotation with an oleic acid emulsion . 29
Mg(OH)2 flotation with an oleic acid emulsion . 3O
Mg(OH)9 flotation with an oleic acid soap
SOlugion . . C 0 O . O O O O C O O O O O O C . 33
Mg(OH) flotation with an oleic acid soap
SOluéion O O O C . O O C I O O C O O O O O O 0 3h
A120 .3H 0 flotation with a lauric acid soap
SO uti n O O O O O O O O O O O O O C O 0 O O O 36
A120 .3H20 flotation with a lauric acid soap
SO ution o e e o e e e e e e e e e o e .0 e e O 37
Mg(OH) flotation with a lauric acid soap
301.11%1 on Q C C C O O O O C O 0 0 C O O O O C O 1+0
Mg(OH)a flotation with a lauric acid soap
solueion . . . . . . . . . . ... . . . . . . . hl
Effect of temperature on flotation of Mg(OH)2 . h3
Effect of temperature on flotation of Mg(OH)2 . hh
Effect of temperature on flotation of A1203.3H20 h?
Adherence of various collector films on gelatinous
aluminum 0 O O O O O O O O 0‘ O O O O O O O O C 51
Adherence of linoleic and lauric acid films on
gelatinous magnesium . . . . . . . . . . . . . S2
Bubble attachment comparison . . . . . . . . . . S7
Flotation efficiency as a function of air pres-
sure with the Sveen-Pedersen Saveall . . . . . 6h
V
TABLE
II.
III.
IV.
V.
VI.
VII.
VIII.
IX.
XI.
XII.
XIII.
XIV.
LIST OF TABLES
PAGE
Metallic hydroxides and hydrated oxides floated
and reagent used . . . . . . . . . . . . . . 12
Reagents tested as collectors . . . . . . . . 19
Hydrated aluminum oxide transmittance data . . 25
Magnesium hydroxide transmittance data . . . . 2?
Magnesium hydroxide floation with an oleic
acid emulsion containing approximately 1.0
ml. per 200 mls. solution . . . . . . . . . 31
Magnesium hydroxide flotation with an oleic
acid soap containing 1.0 ml. oleic acid
per 200 mls. SOlution e o e e e e e e e e I 35
Hydrated aluminum oxide flotation using a lauric
acid soap containing 1.0 gram lauric acid
per 200 mls. of solution . . . . . . . . . . 38
Magnesium hydroxide flotation using a lauric
acid soap solution containing 1.0 gram of
lauric acid per 200 mls. of solution . . . . t2
Effect of temperature on flotation of Mg(0H)
using 5.0 mls. of an oleic acid emulsion 2
containing approximately 1.0 ml. oleic acid
per 200 mls . . . . . . . . . . . . . . . . ES
Effect of temperature on flotation of gelatinous
aluminum oxide using 0.6 mls. of oleic acid
soap containing one part per 200 parts by
VOlumo e e e e e e e e e e e e e e e e e e 0 us
Effect of temperature on flotation of gelatinous
oxide using 0.6 mls. of linoleic acid soap
containing one part per 200 parts by volume . E9
Repeated washing and flotation of gelatinous
aluminm O O O O O O O O 0 O 0 I O O O O 0 0 SB
Repeated washing and flotation of gelatinous
magnesium . . . . . . . . . . . . . . . . . Sh
Analysis of service water supplied to buildings
on the north campus of Michigan State Univer—
sity. This is a typical analysis . . . . . 69
vi
CHAPTER I
INTRODUCTION
The separation, grading, and purification of materials,
is a problemwwifih'which engineers and in particular mining
and chemical engineers are frequently confronted. To solve
these problems vast sums are invested annually by many in-
dustries for milling and screening plants, filters, frac-
tionation columns, settling basins, and many other types of
separation equipment. The separation and purification of
materials is a primary justification for the employment of
thousands of chemical engineers. There is a continual
search for more effective and econdmical means for the separ-
ation and purification of materials.
The principal of flotation provides in some industries,
and in particular the mining industry, an effective, and in
many cases, a very efficient means for the separation of
materials. In the mining industry, where this principle is
currently finding its primary application, it is being used,
each year, for the concentration of 150,000,000 tons of
non-ferrous ore in the Western Hemisphere alone.(h)
The application of this principle is no longer limited
to the minerals industry however. The number of materials
separated or concentrated by flotation has, in recent years,
grown rapidly. Such diverse materials as coal, diamonds,
Sulfur, collodial oil, peas, seeds, paper mill white water
wastes, dyes, certain bacteria, viruses, many types of
industrial wastes, and sewage are being separated by flo-
tation.(7) It appears that the method will come into even
greater use as the horizons of technology and imagination
are extended.
All materials which are not chemically inert may
theoretically be concentrated by air flotation from liquids
in which the finely divided materials are suspended. How-
ever, as is often the case, the breach between that which is
theoretically possible, and that which is at present tech-
nologically feasible, is great.
The primary problem usually associated with flotation
systems is a problem involving surface chemistry. In order
to separate a desired particle by flotation, it is necessary
to form on at least a portion of that particle, a surface
which is sufficiently hydrophobic as to cause the particle
to be held at a gas-liquid interface. It is often necessary
that similar hydrOphobic surfaces be absent from such foreign
particles that are present as impurities. The technique for
bringing about such a condition in the suSpended material
being separated is, in essence, the science of flotation.
The flotation technique, now known as gross flotation,
was first demonstrated by the Norwegian engineer, Nils
Pedersen, and patented in the United States in 1921(11).
Pedersen's machine was also patented in Norway in 192h and
in Germany in 1925. Pedersen's machine was designed to
recover white water waste from the Fourdrinier machines of
the paper industry. This white water contained suSpended
fibers, rosin size, glue, casein, clay, and mineral pig-
ments.
In Pedersen's machine,air at 30-h5 p.s.i.g. was dissolved
in the white water suSpension. After a short time the pres-
sure was released and the air coming out of solution as
myriads of submicroscopic bubbles adsorbed on the surface
of the white water particles,floating them, in a bubble-like
blanket, to the surface of the liquid from whence they were
removed mechanically. Pedersen's development was not
immediately successful.
Pedersen's invention did not prosper until the intro-
duction by Karl Sveen, another Scandinavian engineer, of an
agglomerating material which came to be known as Sveen's
glue. This glue was made from animal glue, rosin size,
alum, and formaldehyde; the formaldehyde serving to prevent
decomposition of the mixture. Sveen glue, when used in
the Pedersen machine, materially aided the flotation process
and the Sveen-Pedersen Saveall, as it became known, mmssoon
adOpted by the paper industry throughout much of Europe.
The Sveen-Pedersen Saveall was introduced into the
United States in 1937. Two years later, August 17, 1939,
(11) presented a very complete description
Ward D. Harrison
of the commercial Operation of the Sveen-Pedersen Saveall
before an assembly of the Technical Association of the Pulp
and Paper Industries. He reported reduction in white water
1+
solids from 9 pounds to 0.3 pounds per thousand gallons in
some cases. The utilization of the Sveen-Pedersen machine
is now common in the United States paper industry. Its use
effects a very considerable economy in material losses and
avoids resultant stream pollution.
New uses are rapidly being found for the Sveen-Pedersen
Saveall.
Among these new usages are: the removal of oil
from brines and water, recovery of fines from synthetic
rubber polymerizing processes, concentration of citrus
pulp, recovery of soap spills, recovery of fish pro-
tein, hydration of fruit skins, seeds, and stems; re-
moval of emulsified oil from railroad round house waste
water, removal of carbon from airplane engine cleaning
water, removal of grease from meat packing wastes, re-
moval of solids from beet sugar waste waters, removal
of starch from water, removal of stillage solids from
winery waste water, removal of fines from fermentation
leps, removal of albuminoids from beet and cane eager
solutions, and removal of fine solids from sewage.
Flotatiqg Applied 32 Problem of Washing Slimy Precipitates
It is necessary in certain processes to filter and
wash the slimy gelatinous precipitates of metallic oxides
or hydroxides. This operation is a very difficult and time
consuming task. Filtration of such precipitates is nec-
. essarily costly. Flotation of these precipitates would
allow simultaneous separation from salution and washing
to be combined in one operation. The demonstration of such
a flotation procedure based on known flotation principles
was a part of the main objective of the present investigation.
Scope 22 the Investigation
The purpose of this investigation was to examine the
possibility of using the gross flotation technique for the
washing of slimy precipitates of metallic hydroxides and
hydrated metallic oxides. This work involved a study of
the kind and amount of effective collector reagents for the
efficient flotation of such precipitates in a machine de-
signed to effect the release of air dissolved in water sus-
pensions of such precipitates at pressures higher than
atmospheric.
The gelatinous precipitates of magnesium hydroxide and
hydrated aluminum oxide were chosen for a detailed study;
these materials were considered to be representative of
oxygenated slimy precipitates. Other hydrated metaflic oxide
precipitates were shown to be amenable to washing by the
gross flotation technique.
CHAPTER II 6
EXPERIMENTAL EQUIPMENT
The primary item of equipment used in this investigation
was a flotation machine especially designed for the project.
(See Figures 1, 2, and 3).
This machine consisted of a pressure chamber built of
standard pyrex glass pipe; this chamber was provided with
an internal agitator. Air, under pressure, was applied to
the base of the machine and bubbled up through the agitated
suspension. The air at 80 p.s.i.g. was brought to the
machine through c0pper tubing. An air filter preceded the
valve regulating the air supply to the machine. This filter
prevented the introduction of entrained oil into the pressure
chamber of the machine.
Air pressure in the machine was regulated by means of
a specially built relief valve. (See Figure h). This valve
consisted of a steel ball bearing which rode on a brass
seat; it was weighted by means of a lever arm resting upon
it. A sliding weight on the lever arm, held in place by a
set screw, served as a pressure adjustment. During Opera-
tion of the machine there was a continual flow of air through
the chamber and contents, since the air supplied to the
machine was at 80 p.s.i.g., whereas pressure in the chamber
was held constant throughout all of the experimental work
at 35 p.s.i.g.
The flotation machine and auxilary equipment.
Figure 1.
Figure 2.
Close-up of lower section of flotation machine.
’!
Figure 3.
Notice clarity of water beneath floated layer. The c0pper
tubing air connection and thermocouple wires are shown here.
The thermos flask containing ice and used as a reference
junction with the potentiometer is also evident.
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The internal agitator assembly consisted of a a" stain-
less steel shaft fitted with four stainless steel impellers
equi-spaced along the shaft. The shaft was supported at
the bottom end by a nylon bearing, and at the t0p end by a
special pressure sealed bearing(5) through which it extended
to the outside of the pressure chamber. Outside, and immed-
iately above the chamber top, the agitator shaft was support-
ed by a pillow block bearing which prevented the application
of a lateral stress upon the sealed bearing. The agitator
shaft was driven through a V-belt connection by means of a
hydraulic speed reducer, which was in turn connected by a
V-belt drive to a % h.p. electric motor. The agitator was
driven at approximately 300 R.P.M.
Materials entered the machine through a %” stainless
steel pipe fitted with a i" stainless steel valve. A funnel
served to direct liquids into the entrance pipe. Liquids
were removed by gravity through a valved %" stainless steel
pipe at the bottom of the pressure chamber. Both the top
and the bottom of the pressure chamber were sealed by stain-
less steel plates, fitted with rubber gaskets. These plates
held the pipes and the agitator shaft bearings. The pressur-
ized air connection was attached to the bottom plate. The
Pyrex pipe aluminum flanges were standard size.
CHAPTER III 11
PRELIMINARY EXPERIMENTAL WORK
Survey gf Metallic Hydroxides and Hydrated Oxides
The first work undertaken was a survey to determine the
floatability of many of the metals forming hydroxides and
hydrated oxides.(17) It was found (see Table I) that the
precipitated hydroxides of aluminum, magnesium, manganese,
chromium, cobalt, cadmium, nickel, zinc, and iron could be
floated using oleic acid as a collector. In the case of
iron, it was found necessary to add a small quantity of
activated silica, in order to make the oleic acid an effec- -
tive collector. The hydrous hydroxide of bi-valent copper
was floated with an emulsion of light maChine oil in methanol
after first activating the precipitate with eosin red dye
which it adsorbs.(18) The flotation was difficult in this
case.
Flotation Experiments with Digested Bauxitg
Attenpts were also made to float the residual red mud
from the digestion of bauxite with caustic. A 50 pound
sample of Suriname bauxite was generously donated for this
work by the Aluminum Company of America.
The digestion was performed in an autoclave according
to directions outlined by Dr. J. W. Newsome,(1u) Chief
of the Alumina and Chemicals Division, of the Aluminum
Company of America. Several reagents were tried as collec-
tors for the red mud but none of those tried was found to
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adding 2.0 grams of sodium hydroxide, and adding water slowly
with mixing until all of the lauric acid had been sanonified
and a final volume of MOO mls. was reached. This lauric
acid sodium soap solution therefore contained 1.0 gram of
lauric acid per 200 mls.
The curve of Figure 12 is somewhat risleading and re-
quires explanation. The curve might be interpreted to
indicate that flotation improved as the ratio of lauric.acid
to Mg(OH)2 decreased. All the evidence available however,
strongly suggests that the ratio of lauric acid to M3{QH)2
floated is high when the total amount of lauric acid present
is low due to the relatively large solubility of lauric
acid in the water solution, and that after the solubility
requirement of lauric acid in water has been satisifed the
behavior is analogous to that of oleic acid as shown in
Figure 1C. In both cases a maximum of flotation is indicated
at definite reagent concentrations.
Figures 13 and 1h show the flotation results obtained
in floating Mg(OH)2 with the same lauric acid soap used in
floating the A1203.mH20 of Figures ll and 12.
Effect of Temperature 2g Efficiency 22 Collector
Figure 15 shows the effect of varying temperature upon
the flotation of Mg(OH)2 using the same emulsion used pre-
viously in obtaining the curves of Figures 7 and 8 for the
flotation of Mg(OH)2. The effectiveness of 5.0 mls. of the
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TABLE IX.
Effect of temperature on flotation of Mg(OH) using 5.0 mls.
of an oleic acid emulsion containing approximately 1.0 ml.
oleic acid per 200 mls.
Initial
Temper- Per Cent Total Mg(c§12 Per Cent 2;
ature Trans- Pleated Total
mittance (Grams; Floated
116 77 1.77 88.5
128 90.5 1.92 96.0
1,411» 9605 1'97 9805
151+ 99.6 1.99 99.5
1.6
emulsion was determined at several different temperatures
and as Figures 17 and 18 indicate the variation of collector
efficiency with temperature is great.
A correSponding temperature effect is shown in Figure
17 in floating hydrated aluminum oxide using the same sodium
soap solution of oleic acid as was used in obtaining the
curves of Figures 9 and 10 for Mg(OH)2. The preparation
of this oleic acid soap solution has been previously de-
scribed. Shown also in Figure 17 is a similar curve obtained
with a linoleic acid sodium soap solution prepared in
exactly the same manner as the previously described oleic
acid soap solution was prepared. The results are shown on
the same plot for comparative purposes._
Repeated Flotation and Washing 2f the Aluminum Oxide and
Magnesium Hydroxide Frecipitates
Washing of the aluminum and magnesium precipitates was
accomplished by the following stepwise procedure:
1. The suspended precipitate was first floated in the
usual manner.
2. One-half of the total volume, or 850 mls. of the
water layer beneath the floated material was then
drained out of the machine.
3. An equal quantity (850 mls.) of fresh water was
then added to the machine. (In the case of Mg(OH)
an additional 20 mls. of 28% ammonia was also 2
adled to maintain pH above lO.h).
h. The material was then refloated in the usual manner
using a ten minute agitation and a ten minute
settling period to complete the cycle.
in
m \ m... sol
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TABLE X.
Effect of temperature on flotation of.gelatinous aluminum
oxide using 0.6 mls. of oleic acid soap containing one part
per 200 parts by volume.
1331‘ mIEEEEEo TEEEEET FTSEEZd
7h 62 1.90 57.6
'75 57 1.70 51.5
95 71 2.23 67.6
95 7h 2.35 71.2
102 70 2.20 66.7
10h 67 2.07 62.8
116 92 3.00 90.8
116 95 3.12 9h.5
121 100 3.30 100.0
126 102 3.30 100.0
#9
TABLE XI.
Effect of temperature on flotation of gelatinous aluminum
oxide using 0.6 mls. of linoleic acid soap containing one
part per 200 parts by volume.
Initial
4—203:- -:-_-_::- Edi-$123333“? ~30 -‘-’-‘-
Tb’fl" mittance m FTSZI‘E‘Jd
72 72 2.25 68.2
91 81 2.60 78.7
93 7h 2.35 71.2
at 91 .2 .98 9o . 3
102 91 2.98 90.3
113 90 2.95 89.u
118 92 3.00 ‘90.8
123 96 3.15 95.0
126 97 3.17 96.0
127 98 3.23 97.8
1&1 3.28 99.h
99.5
50
The curves of Figures 18 and 19 were obtained by
sampling the lower water layer which was removed in Step 2
of the previously listed procedure. Test conditions for
each curve, as marked, are given in Tables XII and XIII.
Notice the nearly parallel behavior of oleic acid as
compared with linoleic acid and also how much better the
collector film adheres to the magnesium precipitate as
compared to the aluminum precipitate. Notice also the poor
adherence of the lauric acid collector in both aluminum and
magnesium flotation and that best results were obtained by
heating the solutions before flotation. By running at
higher temperatures, excellent flotation was assured with a
near minimum of collector.
The dip indicated in the curves shown in Figures 18
and 19 suggest that possibly the first washing caused
particles with collector deficiencies to drOp out.
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Bubble Attachment
The method of gross flotation as used in this work was
different from the usual mineral froth flotation in that
bubble attachment was the result, almost exclusively, of gas
precipitation upon the surface of the floated particles.
In the usual froth flotation of mineral particles, bubble
attachment is the result primarily of collision between the
bubble and mineral particles in t1 -‘t,t d war is (8)
r- u 0 1 10 1e agi.a,e Sicpens on.
In such a system it can be shown that as particle size is
reduced the chances for successful bubble-particle encounter
become much less. is a consequence, systems containing very
small particles are floated with difficulty.
Surprising as it might seem, very small particles are
also difficult to float using the gas precipitation method,
see
N
periments. For example, experiments
CD
as it was used in th
with the flotation of CaCO3 and drigd A1203.nH20 using
linoleic acid soap as collector showed that the waterial
could not beczompletely floated even though an excess of
collector was used and it was run at a high temperature.
These materials, C8603 and A120,.nH 0 (dried), showed
a marked di ference in their {Lynnbility as compared with
the previous gelatinous precipitates. The best results
which could be obtained resulted in a transmittance reading
of 87% in the case of dri7d A1 13.nH20. Similar results
56
were obtained with CaCOB. It was observed in these cases that
there was no appreciable flocculation and that many very fine
particles remained in suSpension upon release of the air
pressure. It thus appears that flocculation is very essential
to the gross flotation method.
Unfortunately the method of gross flotation is non-
selective. All foreign material particles in the suspension
which are not too heavy or dense are floated either by
direct collector activity or indirectly by becoming trapped
or adsorbed by the straining action of the floating floc.(2)
Bubbles are attached to the relatively large floc
particles in gross flotation, whereas in mineral flotation
the particles are attached to relatively large bubbles.
These differences are illustrated below in Figure 20.
Relative Efficiency of Some Organic Acids as Collectors
It appears, from the results given in Table II, that
there are two primary factors to be considered in selecting
a straight chain organic acid as a collector for the oxygenated
metals; they are melting point and solubility.
The melting point of the acid determines, to a large
extent, its diapersibility in solution whereas its solubility
determines the quantity of the acid required. A more soluble
acid is not so effective probably because the film which it
forms is not so hydrophobic in comparison to films formed
by the less soluble acids, and in addition more of the acid
is necessary to satisfy the solubility requirements within
the body of the rigid.
503.625 / 7' 7 /‘7( HME N 7 COMPflR/SON
.-
M/A/f x7571. f2 0777 770M
GROSS FLO 7777770N
[761/95 20
57
58
Keck and Jasberg(12) found from their studies on the
flotative properties of magnetite, that with the saturated
fatty acids valeric, caproic, caprylic, and stearic, flo-
tation increased with the number of carbon atoms. 'Oleic
acid was found to be a better collector than saturated
stearic acid. They suggest that the inferiority of stearic
acid was due to its lack of diapersion.(13) The results
of Table II are in agreement with this suggestion. In
Table II lauric acid was the last saturated soil in the
series of increasing number of carbon atoms which had a
low enough melting point to be sufficiently dispersible at
1150 Fxto be effective as a collector at that temperature.
However from the standpoint of quantity, lauric acid was
only about one-tenth as effective as unsaturated oleic or
unsaturated linoleic acid, due most probably to its greater
solubility. This may be seen from a comparison of Figures
9 and 13.
It is interesting to note that at temperatures above
1150 F oleic acid is equal to or superior to linoleic acid
as a collector according to the results of Figure 17. The
oleic acid film is probably more effective at higher temper-
atures because it is more hydrophobic. At temperatures below
115° linoleic acid is more effective as compared to oleic
acid at the same temperature; linoleic acid appears to be
more readily dispersed than is oleic acid. This increased
effectiveness of linoleic acid may be due to its chemical
59
constitution, or those physical properties which allow it
to be more easily dispersed.
According to Gaudin(9)
In practice where a carboxylic acid or its soap is
required for collection, unsaturated acids such as oleic
acid are preferred. The preference for unsaturated
fatty acids has led to the search for cheap sources of
multiply unsaturated fatty acids such as those of corn
oil, cottonseed oil and fish oil foots. It is believed
that these fatty acids have greater solubility in water
and_a lower melting point than saturated fatty acids
with hydrocarbon chains of equivalent length.
That unsaturated acids are more effective than saturated
acids may well be some function of their solubility. However,
on the basis of these findings it is evident that solubility
is a detriment to collector efficiency. It therefore appears
that the effectiveness of the unsaturated acids such as oleic
or linoleic acids must be explained in some other manner.
In some instances the multiply unsaturated acids are
readily oxidized. To determine whether or not oxidation
during flotation with oleic acid was responsible for its
high efficiency as a collector, Gaudin and Cole(6) floated
fluorite with highly refined oleic acid, extracted the floated
mineral with solvents for oleic acid after inoxidative gentle
acidification, and examined the extracts for the presence
or absence of double bonds. They concluded that oleic acid
was unchanged, even when the mineral which it coated was
floated repeatedly, that linoleic acid which has two non-
-conjugated double bonds, was not effected appreciably more
than oleic acid, but that linolenic acid (three non-conjugated
60
bonds) was measurably altered, even after one single flotation
step. They concluded that the extraordinary utility of these
reagents is related to some property of the compounds other
than the oxidizability of their double bonds.
(10)
The recent work of Hackerman and Makrides suggests
and supports another explanation for the superior results
obtained with unsaturated acids. The only real difference
between a saturated acid such as stearic acid and unsaturated
acids such as oleic and linoleic acids is their comparative
hydrogen deficiency. From the chemisorption viewpoint an
unsaturated double bond possesses an extra pair of sharable
electrons. The sharing of these electrons with positively
charged surface atoms might well explain the greater
efficiency of the unsaturated organic acids as flotation
reagents.
Frothing
As has been suggested previously gross flotation is
somewhat different from the usual froth flotation in the
manner of bubble attachment as illustrated in Figure 20.
The presence of excess froth is completely unnecessary in
this type of flotation. It was observed that the degree
of frothing of the agitated suSpension with added collector
was in no way directly related to the final flotation results
obtained. The appearance of froth even with a collector
such as oleic acid did not necessarily guarantee good final
results, whereas good results were often obtained with a
minimum of froth.
61
Frothing is related to the concentration of a potential
frother in the solution as compared with its concentration
at the gas-liquid interface. This relation is expressed by
the Gibbs equation given here, which relates the two
concentration factors to the rate of change of surface
tension with concentration in the bulk of the fluid.
Gibbs equation:
/“: :9. .95
RT'dc
Whe re, F
difference in concentration between bulk of
liquid and concentration at gas liquid
interface
concentration in bulk of liquid
surface tension
C
xi
R gas constant
T
temperature
(Note: for greater precision activities should be used
in place of the concentration factors in the above
equation.)
If the rate of change of surface tension with respect
to concentration is negative, then f“ is positive and surface
tension is lowered with increasing concentration of material
in the bulk of the fluid. Such a decrease in surface ten-
sion makes a froth or foam more stable, thermodynamically
Speaking, since less energy is required for an extension of
the surface.
Generally, organic substances which are only slightly
soluble are positively or preferentially adsorbed at the
surface whereas inorganic salts are negatively adsorbed.
62
Organic substances which have both a hydrophobic portion
and a polar hydrophylic portion in their molecules are often
good frothing agents. Examples of such materials are pine
oils, cresylic acid, and certain synthetic alcohols. The
organic acids used in this work also acted as frothing agents.
When the minimum of the organic acid required for
effective flotation was used, very little frothing was evi-
dent during agitation. The floated material gave the
appearance of the usual froth as observed in traditional
mineral flotation and only closer examination would reveal
any distinction between the two types of flotation. The
distinction is merely one of structure of the froth or bubble
attachment as shown in Figure 20. Gross flotation, although
different from the standpoint of bubble attachment, is,
strictly speaking, a froth flotation.
pg 33 3 Variable
Consideration has to be given to the effect of pH in
almost every flotation system. In some systems it has been
found that the difference between float and non-float is
merely a matter of one pH unit whereas in other systems the
range may be as great as six pH units.(16)
pH was not studied in this investigation primarily due
to the solubility sensitivity of the materials to pH changes.
The solubility consideration presented an obstacle to such
a study since the method of analysis depended upon the
assumption of constant concentration of the material being
63
floated. To overcome this solubility obstacle different
methods of analysis would have been required.
It is quite likely, that for the flotation of the
aluminum precipitate, that a pH of about 7.0 would have
been found to be optimum. Deshpande and Bhat(3) found that
a pH of seven was Optimum for the flotation of alumina and
Harrison(ll)
reported a pH of about seven as being optimum
for the flotation of white water in which gelatinous aluminum
floc was one of the principal constituents floated.
Li}: m Throgh _t_h_e_ Chamber .
No attempt was made to regulate air flow through the
agitated suspension but it was kept as constant as slight
variations of the building's air supply would allow by
opening the air inlet valve completely during all tests. It
is felt that the total air flow was probably only important
to the extent that it affected agitation of the suSpension.
Air Pressure ig the Chamber
Air pressure in the chamber was kept constant at 35
p.s.i.g. in order that other previously discussed effects
(11) gives the curve shown in
could be studied. Harrison
figure 21 for the relation between air pressure and per cent
efficiency for the flotation of paper mill white water. It
seems quite likely, in View of the fact that aluminum floc
was one of the principal constitutents of the white water
system, for which this curve is given, that this relation
should also hold quite closely for the system of gelatinous
6h
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65
aluminum used in these eXperiments. It would not be sur-
prising to find that the same curve also predicted results
for the flotation of gelatinous magnesium.
Release 2: Air Pressure
From observation of the suSpension upon release of air
pressure from the machine, it appeared that the results
were not appreciably affected by the manner of release pro-
vided the release was not too violent or too slow. If the
release was too rapid it appeared that much air escaped
without effect due to violent agitation of the suspension
after some of the gas had already precipitated upon the
surface of particles, in which case the bubbles were broken
loose and floated free. When the release of air pressure
was too slow, a somewhat similar effect was evident, due
to turbulence introduced by air escaping from the air tube
entering the chamber at the bottom. Both of these diffi-
culties were absent when air release was gradual but not
too slow.
Agitation
Agitation was constant throughout these experiments.
The flotation machine was equipped with a hydraulic variable
speed reducer, but this was run at maximum Speed at all
times. A variation of agitator speed may have had an effect
upon flotation results, especially in view of the assumed
importance of dispersion to collector efficiency.
66
‘Time of agitation was kept conStant at ten minutes.
Both the speed of the agitator and the time of agitation
may have reasonably had some bearing on the size of the floc
which resulted, as well as upon the degree of dispersion of
the collector. It was observed that a finer floc floated
more readily than a course floc.
Washing the Precipitatgs
The procedure for repeated flotation and washing of the
precipitate has been given previously and will not be re-
peated here.
The previous data shown in Figures 18 and 19 and
tabulated in Tables XII and XIII indicate, the best results
were obtained when the materials were floated at higher
temperatures. When higher temperatures were used the loss
of precipitate was held at its lowest level. Unfortunately
the cost of heat is high.and quite probably would preclude
the use of heat in most commercial applications of this
principle.
Examination of Figures 7, 9, ll, 13, and 15 indicate
that in some cases the highest efficiencies are not attained
even with excess collector at temperatures lower than 120°.
Adherence of the collector film is poor at these lower
temperatures.
The contamination caused by an adhering acid film such
as oleic acid or linoleic acid would amount to approximately
0.09% in the case of gelatinous magnesium calculated as
67
Mg(OH)2 and approximately O.ll% in the case of gelatinous
A1203.nH20 calculated as A1203.3H20. Such a slight impurity
would very likely be tolerable in most instances. An adher-
ing acid film could of course be destroyed by calcination.
Even in cases where it was found desirable to use the sodium
soap of the acids as collectors no appreciable sodium should
interfere since it seems reasonable that only the collector
anion is responsible for film formation.
Gross flotation precludes the elimination of insoluble
impurities by this washing procedure due to the non-Specific
nature of the gross flotation method. Only soluble impurities
would be eliminated by such a procedure of repeated flotation
and washing. It may be found possible to eliminate some
impurities by proper control of pH to render them soluble.
This could be a subject for further investigation.
Hardness of Hater and Its Effect Upon Results
A typical analysis of the tap water used in these ex-
periments is given in Table XIV. It is evident that there
is an appreciable amount of hardness due to the presence
of Ca“ Mg“. This total hardness amounted to 339.0 parts
per million as CaCOB.
The Mg‘+ and Ca“ ions were both precipitated almost
completely under the conditions of these tests. A turbidity
of 7h% was measured when the pH, of 1500 mls. of the tap
water used in these eXperiments, was raised to 10.5 by the
addition of 20 mls. of 28% ammonia.
68
Assuming all of the calcium and magnesium was pre-
cipitated, a simple calculation showed that 339 parts per
million of CaCO3 was equivalent to 0.3h5 grams per 1700
mls. as Mg(OH)2.
Since it was known that C‘JOB and MgCO3 also floated
under these test conditions it could only be concluded that
interference by these materials, in this investigation,
was significant. In spite of such interference it was
decided to continue the use of tap water due to the difficulty
of obtaining sufficient quantities of distilled water for
these experiments.
69
TABLE XIV.
Analysis of service water supplied to buildings on the north
campus of Michigan State University This is a typical
analysis.( 5
P.P.M., CaCO3 Equivalent
Silica 9.6
Iron 0.3
Galoium 221.0
Magnesium 118.0
Sodium 18.8
Potassium 1.6
Manganese 0
Carbonate O
Bicarbonate 38h.0
Sulfate 32.6
Chloride 8.6
Fluoride 0.2
Nitrate 1.h
Total Hardness as CaCO3 339.0
CONCLUSIONS
I.
II.
III.
IV.
V.
CHAPTER VII 70
CONCLUSIONS
A machine, similar in principle to the Sveen-Pedersen
Saveall, was shown to be an efficient device for the
flotation of slimy gelatinous precipitates.
Oleic and linoleic acids are excellent collectors for
many slimy gelatinous metallic precipitates.
I
The efficiency of the organic acids as collectors for
these precipitates was shown to be temperature
dependent.
Repeated flotation and washing of the gelatinous pre-
cipitates of aluminum and magnesium was possible
without the addition of more reagent at each flotation
step.
It was found possible to float and wash the gelatinous
precipitates of aluminum and magnesium three times
without appreciable loss of the precipitates provided
a temperature exceeding 1209 F was used in the initial
flotation step.
BIBLIOGRAPHY
10.
ll.
12.
13.
1h.
15.
BIBLIOGRAPHY 71
Campbell, J. M. Private Communication. {1958}
Coleman Model 1h. Spectrgphotometer Igstruction Haggai.
D'Arcy, N. A. American Petroleum I stitute, Tulsa, Okla.
Deshpande, F. K., and G. h. Bhat. "Bubble pick-up
Studies with Alumina," g. Ind. Inst. Science, 37 A,
1A1-e (1955).
Dewitt, C. C. Private Communication. (1957).
Burs-Metallic Corporation, Kalamazoo, Michigan
Gaudin, A. M., and Richard E. Cole. "Double-bond
Reactivity of Oleic Acid During Flotation," Trans.
A.I.M.M.E., 196, Tech. Note lhh-B. (1953).
Gaudin, A. M. Flotation. 2nd ed. New York: Ncfiraw-Hili
Book Company, Inc. 529-‘3. (1957).
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