CA2084570C - Manufacture of ferric sulphate compounds - Google Patents

Manufacture of ferric sulphate compounds

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Publication number
CA2084570C
CA2084570C CA002084570A CA2084570A CA2084570C CA 2084570 C CA2084570 C CA 2084570C CA 002084570 A CA002084570 A CA 002084570A CA 2084570 A CA2084570 A CA 2084570A CA 2084570 C CA2084570 C CA 2084570C
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Canada
Prior art keywords
vessel
liquid phase
ferric
closed vessel
oxidation
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 - Fee Related
Application number
CA002084570A
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French (fr)
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CA2084570A1 (en
Inventor
Jaroslav R. Derka
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Eaglebrook International Group Ltd
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BPM Industries Inc
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Priority to CA000585382A priority Critical patent/CA1336856C/en
Priority claimed from US07/718,780 external-priority patent/US5194241A/en
Priority to US07/718,780 priority patent/US5194241A/en
Priority to US07/765,498 priority patent/US5194240A/en
Priority claimed from US07/765,498 external-priority patent/US5194240A/en
Priority to CA002084570A priority patent/CA2084570C/en
Priority to US07/986,025 priority patent/US5332565A/en
Application filed by BPM Industries Inc filed Critical BPM Industries Inc
Application granted granted Critical
Publication of CA2084570C publication Critical patent/CA2084570C/en
Publication of CA2084570A1 publication Critical patent/CA2084570A1/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/14Sulfates

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Catalysts (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

A process is provided for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation of Fe++ to Fe+++ under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:
1) (see fig. I) , and 2) (see fig. II) wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying the liquid phase including a solution containing Fe++
introduced to the closed vessel, through a reacting cloud comprising NO, NO2 and O2 enclosed in the vapour space of the closed vessel and wherein substantially only Ferric ions is present in the liquid phase in the closed vessel relative to the amounts of Ferric and Ferrous ions prior to the addition of FeSO4.

Description

- ~ ITLE OF THE INVENTION
2C~ 7~) MANUFACTURE OF FERRIC SULPAHTE COMPOUNDS.
FIELD OF INVFNTION
This invention relates to the manufacture of ferric 5 sulphate and other ferric compounds such as hydroxylated ferric sulphate compounds from ferrous sulphate utilizing (NOX) as a catalyst and oxygen as the oxidant. [NOX is known to persons skilled in the art as essentially a mixture of NO and NO2 in undetermined ratios. Thus x is considered to be a number 10 between 1 and 2 inclusive of 1 and 2.]
BACKGROUND OF THE INVENTION
Presently it is known to oxidize FeSO4 to Fe2(SO4)3 by HNO3 (nitric acid) (for example U.S. Patent No. 2,196,584). The reaction is described by the following simplified equation:
6FeSO4 + 3H2SO4 + 2HNO3 -> 3Fe2(SO4)3 + 4H2O + 2NO.
The disadvantage of this process is that the released NO has to be taken out of the reactor, oxidized to NO2, polymerized to N2O4 and absorbed as HNO3. The oxidation of NO
to NO2 has to be performed at low temperatures (below 120~ C.) 20 and is accompanied by the evolution of a substantial amount of heat, requiring large heat exchangers for the removal of this heat. As the reaction itself is relatively slow to reach completion a large reaction space is needed to provide sufficient residence time and the HNO3 recovery section adds 25 complications, is bulky and expensive. Another problem is that it is practically impossible to recover 100% of NOX and the emissions are, due to the poisonous nature of both NO and NO2, environmentally unacceptable.
Another process employed provides for the oxidation of 30 ferrous iron at elevated pH. In this process, it is known that the rate of the oxidation in acidic solutions is negligible for 2C~ O
-all practical purposes, however the reaction proceeds quite rapidly at pH = 5 or higher. This approach has three main disadvantages:
(a) The SO4 ions coming with the FeSO4 have to be neutralized.
(b) The products of oxidation (ferric hydroxide and/or oxides) have to be separated from the products of SO4 neutralization. This operation itself poses a difficult problem which is compounded by the requirements to dispose of the sulphate solution.
(c) Ferric oxides have to be reacted with the full amount of H2SO4 to form Fe2(SO4)3.
Oxidation in an acidic solution by utilizing a catalyst - charcoal has been performed, however the rate of oxidation increases with molar ratio C/Fet and at technically feasible values of this ratio the rate of oxidation is quite low. Attempts to increase the rate by increasing the charcoal content introduces frothing problems and a prohibitive cost of charcoal.
Another large group of processes utilizes oxidation by oxygen (either from air or in elemental form) catalyzed by NOX
dissolved in the oxidized solution in a form of FeSO4*NO.
Typical examples are:
1) United Kingdom Patent No. 17,112, N. McCulloch, 1894, 2) United States Patent No. 4,693,881, R. Miller, 1987, 3) Australian Patent No. 71,741, Y. Mikami, 1974, 4) Japanese Patent No. 49-31638, S. Takada, 1974, 5) Japanese Patent No. 61-286228, Nittetsu Mining KK.
These processes are characterized by low operating temperature (<60~ C.) within the range of stability of FeSO4*NO

' - 3 - ~ C ~ ~
-complex and the oxygen (or air) is generally bubbled through the ~ reacting solution. Oxygen has to enter solution to react with the NO complex thus the rate of reaction is hindered by low solubility of oxygen and the time required for completion of oxidation is very long. Quoting Mikami: "2.5 l. of ferrous sulphate slurry were oxidized for 17 hours". (This is to compare with our oxidation rate of 2.25 l. completely oxidized in 20 minutes.) Miller in his simplest version releases the desorbed NOX with off-gas to atmosphere. Quoting: "none of the NO which reaches the top of the regeneration reactor is recovered".
The process is not environmentally safe as it discharges large quantities of off-gas containing .03-.15% NO.
Miller tries to solve this problem by complicated systems for recovery of the desorbed NO including conversion to and recovery as HNO3.
This is to compare with my system where NO is permanently closed in the reactor gas space and only a small bleed-off stream (approximately 3 m3/h), after removal of NO by feed slurry, leaves the process.
It is therefore an object of this invention to provide an improved process for the manufacture of ferric sulphate and other ferric compounds such as hydroxylated ferric sulphate compounds.
It is a further object of the invention to provide such process which is very efficient and environmentally safe.
Further and other objects of this invention will be realized by those skilled in the art from the following summary of invention and detailed description of the embodiments thereof.

;70 - ~M~y OF THF INVTNTION
According to one aspect of the invention, there is provided a process for the manufacture of ferric sulphate compounds (including ferric sulphate and hydroxylated ferric sulphate compounds) from ferrous sulphate (in one embodiment crystals, in another embodiment with the addition of pickle liquor) by the oxidation of Fe++ to Fe+++ under pressure utilizing (NOX) as a catalyst and commercial oxygen in a closed vessel having a liquid phase and a vapour phase wherein the liquid phase comprises substantially (in one embodiment at least about 95%) Ferric ion relative to the Ferric and Ferrous ions present in the vessel prior the addition of Ferrous ion.

The process comprises the following reactions (1) NO + 2 ~2 --> NO2 and (2) nFeSO4 + 2 H2S~4 + 2 (NO2) ->
Fen(S04) ~ (OH)y + 2 H20 + 2(NO) wherein n is any integer greater than, or equal to, two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n. Fen(SO4) ~ (OH)y is Fe2(SO4)3 when n is 2 and y is 0. Thus the process comprises the following reactions:
1) NO + 2~2 -> NO2, and 2) 2FeSO4 + H2SO4 + NO2 -> Fe2(SO4)3 + H2O + NO.
Similarly the following ferric sulphate compounds have been produced by the same process steps (with appropriate modifications to yield the desired product);

(a) Fes(SO4)7(OH), where y = 1,n = 5 2[5(FeSO4) + 2 H2SO4 + 2 N~2] ~>
2[Fes(SO4)7(OH) + 2 NO 2 2 (b) Fe6 (S04)8(OH)2, where y = 2, n = 6 _ [6FeSO4 + 2 H2SO4 + 3NO2] ~>
F6(S~4)8(OH)2 + 3N0 + H20] and (c) Fe7 (SO4)10(OH), where y = 1, n = 7 2[7 FeSO4 + 3H2SO4 + 2 (NO2)] ->
2[Fe7(SO4)l0(oH) +2 NO 2 ( 2 According to another aspect of the invention there is provided a process for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation between about 70~ C. to about 150~ C. of Fe++ to Fe+++
under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:
1) NO + 2O2 -> NO2, and 2) nFeS04+( 2 )H2SO4+ 2-N~2 -> Fen(S04) ~ (OH)y +(~ )(H2~)+ 2--NO

wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than, zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying the liquid phase including a solution containing Fe++
introduced to the closed vessel, through a reacting cloud comprising NO, NO2 and ~2 enclosed in the vapour space of the closed vessel and wherein substantially (in one embodiment at least about 95%) only Ferric ion relative to the amounts of Ferric ion in Fen(SO4) ~ (OH)y and ferrous ion (added as Ferrous Sulphate) is present in the liquid phase in the closed vessel prior to the addition of FeSO4 preferably through the reacting cloud in the vapour phase and preferably by spraying - 6 - ~ C ~ ~

'~through the reacting cloud in the vapour phase. The liquid phase in one embodiment fills at least 3 of the vessel prior to the addition of Ferrous ion. Preferably the Ferrous Sulphate is added to the vessel by spraying through the reacting cloud in the vessel. However where not feasible (because of the physical condition of the ferrous sulphate (containing stones, which may damage the circulation pump) it may be added to the vessel by any means and the liquid phase containing the ferrous only sprayed through the vapour phase.
Thus according to another aspect of the invention there is provided a process for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation between about 70~ C. to about 150~ C.
of Fe++ to Fe+++ under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:

1 ) NO + 2O2 ~> NO2, and 20 2) nFeSO4 + ( 2 )H2so4 + 2--NO2 ~> Fen (SO4)~(oH)y + ( 2 Y) ~H20) + 2NO

wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying a solution containing Fe++ through a reacting cloud comprising NO, NO2 and ~2 enclosed in the vapour space of the closed vessel and wherein the liquid phase fills at least 1 of the vessel and substantially only Fe~(SO4) ~ (OH)y is present in the liquid phase in the closed vessel prior to the addition of ., ~ 7 ~ ~ ~ ~?~70 ~ - FeSO4 and wherein the liquid phase is sprayed through the vapour phase.
Thus according to another aspect of the invention there is provided a process for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation between about 70~ C. to about 150~ C.
of Fe++ to Fe+++ under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:

1 ) N0 + 202 -> N02, and 2) nFeS04 + ( 2 )H2S04 + 2N02 -> Fen (S04)~0H)y + ( 2 Y) ~H20) + 2 N0 wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying a solution containing Fe++ through a reacting cloud comprising NO, NO2 and ~2 enclosed in the vapour space of the closed vessel and wherein the liquid phase fills at least 1 of the vessel and substantially only Fen~SO4) ~ OH)y is present in the liquid phase in the closed vessel during the addition of FeSO4 and wherein the liquid phase is sprayed through the vapour phase.
Preferably the Fe++ ion (for example FeSO4) is introduced to the closed vessel through the reacting cloud in the vapour phase and preferably by spraying.
Thus according to another aspect of the invention there is provided a process for the manufacture of ferric 7~
~ ~sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation between about 70~ C. to about 150~ C.
of Fe++ to Fe+++ under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:

1) NO + 202 -> N02, and 2) nFeS04+( 2 )H2so4+2-No2 ~~ Fen(S~4) ~ (0H)y +(~ )(H2~) + 2-NO

wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than, zero (O) and less than 3n and wherein the oxidation of Fe++ is affected by spraying the liquid phase including a solution containing Fe++
introduced to the closed vessel, through a reacting cloud comprising NO, N02 and ~2 enclosed in the vapour space of the closed vessel and substantially (in one embodiment at least about 95%) only ferric ion relative to the amounts of Ferric ion in Fen(S04) ~ (OH)y and Ferrous ion (for example added as ferrous sulphate) is present in the liquid phase in the closed vessel during the addition of FeS04 once again preferably through the reacting cloud in the vapour phase. Once again preferably the ferrous sulphate is added to the vessel by spraying through the reacting cloud in the vessel. However where not feasible (because of the physical condition of the ferrous sulphate (containing stones) which may damage a circulating pump used) it may be added to the vessel by any means and the liquid phase only sprayed. Once again in one embodiment the liquid phase fills at least 3 of the vessel.

- 9 ~ o Once again oxidation of ferrous iron is essentially accomplished in the vapour phase in the reactor which preferably comprises a single vessel.
In the reactor NOX is trapped in the vapour phase (space) above the solution. The present NO then rapidly reacts with the supplied oxygen according to the reaction:
1) NO + 202 -> N~2.
The solution containing the FeS04 introduced to the circuit or vessel is most preferably sprayed through this "reacting cloud" (the vapour phase essentially comprising NO, N02 and oxygen), also cooling the reacting gas by removing the heat of reaction and reacting with formed NOx:
2) n(FeSO ) + n-Y H SO + n NO >
Fen(S04) ~ (0H)y + 2 H20 + 2 NO

for example 2FeS04 + H2S04 + N02 -> Fe2(S04)3 + H20 + NO.
The NO released by reaction 2) is immediately available for reaction 1). NOx acts as a catalyst in the oxidation process.
The temperature in the reactor is maintained above the point of decomposition (theoretically 60~-65~ C.) of the FeS04*NO complex (which at lower temperatures is stable and is formed at such lower temperatures). Thus NO produced by reaction 2) is released back to the reacting cloud rather than being oxidized in the solution with the consequent low rate of reaction due to the low solubility of oxygen. The oxidation of NO in the gas phase is a relatively fast well-defined reaction.
The produced solution containing traces of NO is denitrated in a NOx desorption vessel by bubbling of feed oxygen through the solution before it is used in the reactor for 2C~570 ~ '~oxidation. The stream of oxygen then carries the desorbed NO
back to the "reacting cloud" in the vapor phase - space of reactor.

The produced ferric compound in solution for example Fe2(SO4)3 solution for example may be drawn from the vessel and the ferrous compound precipitated, filtered and stored. Thus according to another aspect of the invention, the process is preferably carried out continuously with the amount of ferric solution removed from the vessel being the same as the amount of Ferrous Sulphate and other materials added.
In another embodiment the oxidation may be carried out continuously in different vessels connected one to the other (liquid phase overflowing to next vessel and vapour phases being interconnected and in communication with one another) or in another embodiment may be carried out in a batch in one vessel.
The materials may be added in a sluice tank (FeSO4 and water) and mixed and then fed for continuous processing or batch processing. The H2SO4 + NOX make-up (HNO3) are added directly to the reactor.
In the batch process, the oxygen stream from the denitrator may be also added to the reactor. When the reactions are completed producing Fen(SO4) ~ (OH)y for example Fe2(SO4)3, the Fe2(SO4)3 solution is removed.

To produce batches successively in the same vessel, only part (for example 3) of the volume is removed, and the remaining portion (for example 3) is left. This heats the incoming slurry to the temperature required for initiation of the oxidizing reaction. For the reaction to proceed quickly, the temperature should preferably equal or exceed 90~ C. Thus " .. ~ 0 ~the remaining solution provides the temperature for the initiation of the reaction and the "Heat of Reaction" heats the materials added to the reactor. Additionally the final product Fen(SO4)3 (OH)y remains in the solution to keep the NOx out ( n2-Y) of the solution and in the vapour phase (NOx has low solubility in the product Fen(SO4) ~ (OH)y). A small portion of gases present in the vapour phase above the slurry solution are bled off to facilitate the removal of any inert gas present and returned to the sluice tank for mixing with the slurry.
The withdrawn ferric sulphate compound solution is denitrated in NOX desorption vessel (denitrator) by bubbling oxygen through the solution and subsequent cooling. The solution may then be filtered and sent to product storage.
The heat recovered from the product cooling heat exchanger may be used for preheating of water or pickle liquor needed for preparation of feed slurry.
In one example a slurry of Ferrous Sulphate (to be added to the vessel) is prepared in a "Sluice Tank" by weighing the corresponding amount of crystals and water and subsequently transferred to a feed tank. From the feed tank the slurry is continually pumped by a metering pump to the vessel. Sulphuric acid is metered to the reactor as required for the selected F4 ratio.
Solution from the reactor is recycled through spray nozzles, thus allowing an intimate contact between solution and the reacting cloud of NOx, Oxygen mixture.
The reacted solution, containing only traces of Fe++
may leave the reactor by gravity and may in a denitrator be ~c~ o stripped of dissolved NOx by purging with Oxygen. The mixture of Oxygen and the stripped NOx is then returned to the reactor.
The solution level in the denitrator and reactor vessel is controlled by controlling the rate of solution (liquid phase) discharge.
FOR COLD START UPS:
The slurry from the Feed Tank and the proportional quantity of Sulphuric Acid may be fed to the reactor until the mixture amounts to approximately 1/2 of the regular liquid volume. After addition of Nitric Acid the mixture is allowed to oxidize, (continuously recycling with spray nozzles running).
When approximately substantially all (something of the order greater that about 95-98%) Fe++ is oxidized to the Ferric form the rate of reaction marks a substantial increase. After completion of the oxidation (most NOx is in the vapour phase (gaseous part) of the reactor because NOx is substantially insoluble in Fe2(SO4)3 a continuous feed of the slurry and proportional feed rate of Sulphuric Acid are started. From this moment the operation is continuous and the reaction is running at such high rate that the product does not contain a detectable quantity of Ferrous Iron. The Fe++ is oxidized in the vapour phase without detectable Fe++ in the liquid phase.
BRIFF DESCRIPTION OF THE DRAWINGS
The invention will now be illustrated with reference to illustrated processes according to embodiments of the invention.
Shown schematically in Figure 1 is a flowsheet illustrating embodiments such processes.
Particulars of a continuous process is illustrated in Figure 2.

- 13 - 2C~5~0 Particulars of a continuous process is illustrated in Figure 3.
DETAILED DESCRIPTION OF PREFFRRED F~BODIMENTS OF THE INVENTION
The invention is illustrated with reference to ferric sulphate manufacture. The processes illustrated apply equally to the manufacture of hydroxylated ferric sulphate compounds.
Ferrous sulphate crystals are, after delumping in a suitable crushing device such as a roller mill (position A), transported by screw conveyor (position B) as stream 1 into a sluice tank (position C). In this tank a suitable slurry is formed by an addition of the required amount of water (stream 2). Instead of water a pickle liquor (stream 15) may be used with consequential savings in crystals and sulphuric acid.
A slurry of correct composition (stream 5) for the reaction:
2FeSO4 + H2SO4 + 2O2 = Fe2(SO4)3 + H2O

is fed (stream 7) as well as sulphuric acid (stream 3) and occasionally HNO3 make-up (stream 4) to a reactor (position E) which can be either continuous - flowsheet (Figure 1) Details A
and B, or batch - Detail C. Detail A illustrates a reactor where a single closed vessel is divided into compartments with the slurry and sulphuric acid added upstream of the vessel and oxygen and HNO3 make-up added downstream. The same with Detail B which illustrates three separate vessels E1, E2, and E3 whose vapour phases are connected and whose liquid phases overflow counter-currently to gas phase - slurry added to upstream vessel E1 with oxygen downstream at vessel E3. With respect to Details A, B and C, position G acts as the denitrator.
In the reactor, oxidation under pressure by oxygen (stream 14) takes place, NOX acting as the catalyst of - 14 - 2~ 7~

oxidation. The function of NOX can be expressed in a simplified - form as:
1) NO + .5 ~2 = NO2~
and the ferrous iron is oxidized:
2) 2FeSO4 + H2SO4 + NO2 = Fe2(SO4)3 + NO + H2O.
The reaction 1) takes place in the reacting cloud consisting of NOX, ~2 and water vapour, located in the vapor space of the reactor. There the produced NO2 is contacted by spray of the liquid phase and the reaction 2) proceeds.
The product ferric sulphate solution (stream 8), with some NOX dissolved in it due to high partial pressure of NOX in the reactor, is denitrated in the NOX removal vessel (position G), by purging the solution with bubbles of oxygen required for reaction (stream 13). The oxygen with desorbed NOX is then fed to the reactor (stream 14). The NO free solution (stream 9) is cooled in heat exchanger (Hx) and sent to a pump tank (position K) and pumped (stream 10) through a clarifier filter (position H) to storage (stream 11). Heat removed in the heat exchanger is used for preheating liquids (water or pickle liquor) for slurry preparation. As commercial oxygen always contains some nitrogen, its accumulation in the vapour space of the reactor is avoided by a small bleed-off stream (stream 12). This bleed-off stream is in one application sent to the bottom of the sluice tank (position C) where NOX is removed by contact with FeSO4 slurry in the sluice tank. This step utilizes the formation of nitrosyl ferrous sulphate in a FeSO4 solution at temperature <60~ C. for the absorption of NO. The NOX catalyst is then returned to the reactor with the feed slurry (stream 7) introduced through the vapour phase.
In other applications the NO containing gas (stream - 15 - ~G~5~0 _ 13) is scrubbed in a ferrous sulphate scrubber (position D) by FeSO4 slurry (stream 6) because on contact the FeSO4 dissolves the NOX returning it to sluice tank (position C) and subsequently to reactor (position E). NOX free gas, for additional safety, leaves the process through a caustic scrubber. Thus N2 (nitrogen) and ~2 (oxygen) are permitted to leave to atmosphere.
Typical operating parameters:
1) Sluice Tank:
t - ambient, maximum - 60~ C.
2) Reactor:
temperature - above decomposition temperature of FeSO4*NO complex and preferably about 70~ C. to about 150~ C
- most desirable 90~-120~ C.
pressure - 20-100 psig, - preferably 40-60 psig.
3) Product - ferric sulphate solution:
typical - 190 g. Fe/1, range - 60-250 g. Fe/1.
In the continuous processes of Details A and B, the volume of Fe2(S04)3 and H2SO4 being removed (discharged) corresponds to the volume of FeSO4 and being added through the vapour phase. Fe2(S04)3 solution [without Fe++ or only trace amounts of Fe++] is present at the start in the liquid phase to increase the rate of the reaction.
With respect to Detail C (which depicts a batch process), when Fe2(SO4)3 is to be withdrawn, it is preferable - 16 - ~ 70 - ~ 2 that only 3 of the volume is removed. The remaining 3 volume containing essentially Fe2(S04)3 is usually at a temperature exceeding 90~ C., of a temperature at which the reaction proceeds quickly, and thus provides the heat of reaction to cause added cold materials to react quickly to oxidize Fe++ to Fe+++. As well the Fe2(S04)3 left in the liquid phase keeps NOx in the vapour phase to enable increased rate of reaction due to the decrease in solubility of NO (product of Fe oxidation) in the Ferric Sulphate. In that case more NO is available for oxidation in the gaseous phase.
Solution accumulates in the reactor (detail C). On reaching the high level, the feeding of slurry or solution is stopped and on completion of the oxidation, the product (solution) is released through denitrator (position G) where the product is purged by a stream of oxygen passing from position G
into reactor (position E) displacing liquid volume in the reactor (position E).
With reference with Figure 2, there is illustrated schematically a method of oxidation of the Ferrous to Ferric. A
slurry of Ferrous Sulphate is prepared in "Sluice Tank" 20 by weighing the corresponding amount of crystals and water and subsequently transferring the crystals and water along streams 22 and 24 to sluice tank 20. The ferrous sulphate slurry is then transferred by pump 26 to feed tank 28. From the feed tank 28 the slurry is continuously pumped by a metering pump 30 towards the reactor along stream 37. Sulphuric acid is metered from storage 32 to the reactor 34 as required for the selected F4 ratio by metering pump 36 along stream 33. The mixture is sprayed through the vapour phase 34A in reactor 34 through spray nozzles 40 (stream 37). This is permitted where the "slurry" is - 17 - ~G~7 clear of stones which can otherwise damage the equipment. If - the slurry is heavily contaminated by stones the slurry is dumped directly into the reactor vessel.
Solution from liquid phase 34B of the reactor recycled through stream 44 into stream 37 through spray nozzles 40, thus allowing contact between the liquid phase and the reacting cloud of NOx, Oxygen mixture.
The reacted solution, containing only traces of Fe++
leaves the reactor by gravity through stream 46 and is in denitrator 48 stripped of dissolved NOx by purging commercial Oxygen fed along stream 50. The mixture of Oxygen and the stripped NOx is fed to reactor 34 along stream 52. The Fe2(S04)3 product is then removed along stream 54 for cooling (precipitation if desired) storage and use.
The solution level in the denitrator and reactor is controlled by controlling the rate of solution discharge. Thus the volume of liquid phase containing essentially Fe2(S04)3 [with but trace amounts of Fe++ (if any)] removed or discharged along stream 46 corresponds to the volume of materials added to the reactor.
FOR COLDS START UPS:
The slurry from the Feed Tank 28 and the proportional quantity of Sulphuric Acid may be fed to the reactor 34 until the mixture amounts to approximately 1/2 of the regular liquid volume. After addition of Nitric Acid the mixture is allowed to oxidize (continuously recycle with spray nozzles running). When in excess of 95% of Fe++ (usually in the order of at least about 98%) is oxidized to the Ferric form the rate of reaction marks a substantial increase. After completion of the oxidation (most NOx is in the vapour phase (gaseous part) of the reactor because - 18 - ~ C ~ ~70 NOx is substantially insoluble in Fe2(SO4)3) a continuous - Fe2(SO4)3 feed of the slurry and proportional feed rate of Sulphuric Acid are started. From that moment the operation is continuous and the reaction is running at such a high rate that the end product discharged along stream 46 does not contain a detectable quantity of Ferrous Iron.
The essentially Fe2(SO4)3 containing liquid phase may also be used initially and the reaction may start out at a high rate of reaction.
In a typical example, slurry is prepared by weighing 20028 lbs of Ferrous Sulphate crystals containing 19% of Iron and combining it with 7074 lbs of water. This slurry is fed at a rate of 237 lbs/min to the reactor 34 together with 25.1 lbs of Sulphuric Acid per minute.

Under these conditions the solution is produced at a rate of 21 gallons/min, the Fe molar ratio is 1.4.

With reference to Figure 3, the 2400 gallon batches of slurry are prepared in a sluice tank 100 by mixing the crystals of FeSO4 * 7 H20 (stream No. 1) with the required amount of hot water (stream No. lOb) and the resulting slurry is then heated by direct steam (stream No. 11) to a temperature of approximately 126 deg. F.
The heated batch of slurry is then transferred (stream No. 2) to the feed tank from where it is continuously fed (stream No. 3) with metered amount of sulphuric acid (stream 7) to an oxidizing reactor. The nitric acid - source of NOX
catalyst (stream No. 8) is added as required. The ferrous sulphate is oxidized by oxygen in the reactor according to the following reactions:

a) 2FeSO4 + H2SO4 + NO2 --> Fe2(S~4)3 + H2O + NO

- 1 9 - ~C~70 ~ '~ 2NO + ~2 --> 2 NO2 - The oxygen for reaction (b), (stream No. 9), is first utilized for stripping the dissolved N~x from the oxidized solution in the denitrator it then proceeds to the reactor carrying the stripped NOX with it. The NOX stripped from the solution is thus returned to the reactor to fulfill its role of a catalyst, without any emissions to the atmosphere.
The oxidized solution from the denitrator (stream No.
4) is cooled in one of two heat exchangers (HX) before proceeding to storage (stream No. 5). The first HX 100 utilizes product heat for preheating of sluice water (sump water and Pickle liquor). This cooling water (stream No. 10) is provided in the quantity which yields an outgoing water temperature of approximately 194 deg.F (stream No. 10a). Hot water is accumulated in the hot water tank and utilized for preparation of the feed slurry (stream No. 10b). This arrangement achieves an energy saving and minimizes the steam consumption for slurry heating. When the hot water tank is full, the product is cooled in the second HX 102 by city water (stream No. 15) which after the use is sent to sewer (stream No. 16) unless some other, in-plant use is found.
Any spillage from the process area and drainage from the crystal storage area will be collected in a sump system and recycled (stream No. 24) to the sump tank for use in the process, effectively eliminating any effluents from the plant.
Oxygen consumed in the reactor contains traces of inerts (mostly N2). A small bleed-off stream (stream No. 27) is required to prevent the accumulation of inerts in the reactor vapor phase.
Because the solubility of NO in the FeSO4 solution is very high the bleed-off stream is first stripped of NOX by bubbling through FeSO4 slurry in the feed tank. The absorbed NOX is then - returned to the reactor with the slurry feed.
Both the sluice and feed tanks are vented (stream No.
18) through the Pickle liquor scrubber to atmosphere. Any traces of NOX which were not absorbed by the feed slurry are absorbed by the cold Pickle liquor (stream No. 22a) recycled through the scrubber. To keep the solution cool the recycle is cooled in a heat exchanger cooling water (stream No. 25) which after the use is sent (stream No. 26) to drain. The spent Pickle liquor is subsequently sent to the suction of reactor feed pump (stream No. 21) thus returning to the reactor any NOX
that escaped.
If it is desired to utilize pickle liquor as a source of iron and sulphuric acid, it will be pumped from the storage tank to sump tank only if there is shortage of sump water for process purposes.
The product is loaded from a storage (stream No. 6) to either rail cars or tank trucks.
With respect to the process illustrated in Figure 3, reactor vessel is 3000 gallons, of which 1500 gallons is the liquid phase, 25 gallons of slurry is added to the reactor and 25 gallons of Ferric Sulphate solution produced is removed per minute. 250 gallons are sprayed through the vapour phase per minute. For cold start ups, 820 gallons are put into vessel and when the production of ferric sulphate proceeds rapidly, the volume is increased until the 1500 gallon operating amount is reached.
The following hydroxylated ferric sulphate compounds have been made by carrying out the process steps in Figure 3.
The concentration of the ferrous sulfate and sulfuric acid are - 21 - ~G~70 ~ '~changed to produce the proper stoichiometric ratio for each specific compound.The temperature, the pressure and the reaction time are also adjusted within the ranges specified in the patent application.
Fes(S04)70H where n=5 and y=1 Fe6(S~4)8(~H)2 where n=6 and y-2 and Fe7(S04)100H where n=7 and y=1 Thus processes for producing ferric sulphate compounds of the generic formula;
Fen(S04) ~ (OH)y have been described by oxidation of ferrous sulphate in accordance with the equation:
nFeS04 + n2Y(H2S04) + 2(NO) ->
Fen(S04) ~ (OH)y + 2(NO) + 2 (H20) As many changes can be made to the embodiments of the invention without departing from the scope of the invention, it is intended that all material contained herein be interpreted as illustrative of the invention and not in a limiting sense.

Claims (18)

1. A process for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation of Fe++ to Fe+++ under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:

1) , and
2) wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying the liquid phase including a solution containing Fe++
introduced to the closed vessel, through a reacting cloud comprising NO, NO2 and O2 enclosed in the vapour space of the closed vessel and wherein the amount of the Ferric in the present in the liquid phase relative to the amount of Ferric and Ferrous ion prior to the addition of FeSO4 is about 95%-98%.

2. The process of Claim 1 wherein the liquid phase fills at least about 1/3 of the vessel.
3. A process for the manufacture of ferric sulphate compounds from ferrous sulphate in a closed vessel containing a liquid phase and a vapour phase, the process comprising the oxidation between about 70° C. to about 150° C. of Fe++ to Fe+++
under pressure utilizing commercial oxygen in the closed vessel using NOx as a catalyst where x is a number between 1 and 2 inclusive of 1 and 2 and wherein the process comprises the following reactions:

1) , and 2) wherein n is any integer greater than or equal to two (2) and y is any integer which is equal to, or greater than zero (0) and less than 3n and wherein the oxidation of Fe++ is affected by spraying a solution containing Fe++ through a reacting cloud comprising NO, NO2 and O2 enclosed in the vapour space of the closed vessel and wherein the liquid phase fills at least 1/3 of the vessel and wherein the amount of the Ferric in the present in the liquid phase relative to the amount of Ferric and Ferrous ion prior to the addition of FeSO4 is about 95%-98% and wherein the liquid phase is sprayed through the vapour phase.
4. The process of Claim 3 wherein the process is carried out continuously in one vessel.
5. The process of Claim 4 wherein FeSO4 and water are added in a sluice tank and mixed and the resultant solution is added to the vessel.
6. The process of Claim 5 wherein the solution is supplied to a denitrator where oxygen is supplied to denitrate said solution and the resultant gas is then passed to said vessel from the denitrator.
7. The process of Claim 3 wherein successive batches are produced in the same vessel, and part of the volume of the earlier batch is removed leaving a portion comprising substantially only .
8. The process of Claim 1 wherein the process is carried out continuously in the one vessel.
9. The process of Claim 2 wherein the process is carried out continuously in the one vessel.
10. The process of Claim 1 wherein y is O and n is 1 thereby producing ferric sulphate.
11. The process of Claim 3 wherein y is O and n is 1 thereby producing ferric sulphate.
12. The process of Claim 4 or 8 wherein y is O and n is 1 thereby producing ferric sulphate.
13. The process of Claim 1 wherein the compound produced is selected from the group of compounds consisting of Fe5(SO4)7(OH), Fe6(SO4)8(OH)2, and Fe7(SO4)10(OH).
14. The process of Claim 3 wherein the compound produced is selected from the group of compounds consisting of Fe5(SO4)7(OH), Fe6(SO4)8(OH)2, and Fe7(SO4)10(OH).
15. The process of Claim 4 or 8 wherein the compound produced is selected from the group of compounds consisting of Fe5(SO4)7(OH), Fe6(SO4)8(OH)2, and Fe7(SO4)10(OH).
16. The process of Claim 1 or 3 wherein Fes(SO4)7(OH) is produced.
17. The process of Claim 1 or 3 wherein Fe6(SO4)8(OH)2 is produced.
18. The process of Claim 1, 2 or 3 wherein Fe7(SO4)10(OH) is produced.
CA002084570A 1988-12-08 1992-12-04 Manufacture of ferric sulphate compounds Expired - Fee Related CA2084570C (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
CA000585382A CA1336856C (en) 1988-12-08 1988-12-08 Manufacture of hydroxylated ferric sulphate compounds
US07/718,780 US5194241A (en) 1988-12-08 1991-06-21 Manufacture of hydroxylated ferric sulphate compound
US07/765,498 US5194240A (en) 1988-12-08 1991-09-26 Manufacture of ferric sulphate
CA002084570A CA2084570C (en) 1991-06-21 1992-12-04 Manufacture of ferric sulphate compounds
US07/986,025 US5332565A (en) 1988-12-08 1992-12-04 Manufacture of ferric sulphate compounds

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
US07/718,780 US5194241A (en) 1988-12-08 1991-06-21 Manufacture of hydroxylated ferric sulphate compound
US07/765,498 US5194240A (en) 1988-12-08 1991-09-26 Manufacture of ferric sulphate
CA002084570A CA2084570C (en) 1991-06-21 1992-12-04 Manufacture of ferric sulphate compounds

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