NITRIC ACID RECONSTITUTION
Field of the Invention:
The present invention relates to a process for recovering and reconstituting nitric acid in a nitric acid process for the extraction of alumina values from clay and more specifically to an improved method for reconstituting N0x gases produced in such a process.
Background of the Invention:
In order to provide an economically useful nitric acid extraction process for alumina, the nitric acid must be recovered from the total process in sufficient quantity as to provide a high percentage of acid recirculation. It is known in the art that substantial nitric acid may be recovered by direct condensation of HNO3 in the decomposition step of such process. Such recovery recycles about 67% of the nitric acid used in the process. However, substantial amounts of the acid exits other stages of the decomposition in the form of N0χ gases.
The recovery of nitric acid solutions from nitrous gases produced by the catalytic combustion of ammonia in air is a well-known art that is practiced commercially around the world. The basic process comprises contacting the ammonia oxidation gases at a pressure of 3 to 6 atmospheres absolute, or even higher, in a bubble cap-tray absorption column containing of the order of a hundred trays in counter current relationship with a supply of water introduced at the top of the column. Variations of the technology are concerned substantially with design of the bubble cap trays, oxidation of the ammonia under pressure, or oxidation at about atmospheric pressure to reduce catalyst consumption followed by the compression of the cool gases, the recovery and re-use of the heat produced in the ammonia oxidation reaction and
especially recently methods of reducing the approximately 1,000 ppm N0χ concentration in the tail gas before releasing this gas to the atmosphere.
The chemistry of the conversion of N0χ gases to nitric acid in solution is generally considered as consisting of 2 overall reactions which serve to define the mass balance between the liquid a vapor streams. Reaction 1: 3N02(g) + H20(1) = 2HN03(aq) + N0(g) which occurs principally in the liquid phase and reaction 2: 2NO(g) + O2(g) = 2NO2(g) which occurs substantially in the gas phase. The rate of reaction 1 is thought to depend primarily upon the rate of absorption of NO2 into the liquid stream which depends upon the partial pressure of N02 in the gas stream and is thus slowed down by the presence of large quantities of inert gases such as N2, and concentrations of NO in the gas phase which tend to drive reaction 1 in the reverse direction. Once the NO2, has been absorbed the reactions in the liquid phase appear to proceed at satisfactory velocities. The rate of reaction 2 is proportional to the product of the square of the partial pressure of NO and the partial pressure of O2 and can be quite slow in the presence of large amounts of inert gases such as N2. In the ammonia oxidation process for making nitric acid the feed gases from the oxidizer comprise on the order of 70 volume percent N2 and the proportion of N2 increases as the NOχ gases are absorbed from the gaseous stream. Additional N2 is added with air to provide some oxygen in the tail gas to drive reaction 2 toward completion. Thus, although nitric acid has been recovered from ammonia oxidation gases at about atmospheric pressure using 2 or 3 absorption towers in series it has been found more economical to compress the gases to 3 to 6 atmospheres absolute so as to increase the partial pressure of the reacting gases sufficiently to permit
carrying out the reconstitution in a single tall column. On the other hand NOχ gases produced by the thermal decomposition of aluminum nitrate material in properly constructed, indirectly-heated decomposers contain little or no inert gases. A typical composition of such a gas, before any air in-leakage, is about 25 volume percent of (NO2 + NO), about 12 1/2 volume percent O2 and about 62 1/2 volume percent water vapor. Since in the absorption column water vapor is absorbed in the liquid stream much more rapidly than NO2 the concentrations of the reacting gases increase during passage through the absorption column so that the same or even higher rates of Reactions 1 and 2 may be achieved at near atmospheric pressure as can be achieved with ammonia oxidation gases at elevated pressures.
Since both Reactions 1 and 2 are highly thermic and the easily reversible Reaction 1 can begin converting HNO3 from the acid solution to NO2 in the gas at temperatures as low as 150 to 180°F, depending upon the concentration of HNO3 in the liquid and of NO in the gas phase, the removal of heat from the absorption column is of major importance. It is known in the art to remove this heat either by placing water-cooled cooling coils in the liquid layer maintained on the upper side of the bubble cap trays or to withdraw a portion of the liquid from each of a number of trays in the column, pass the liquor through individual heat hangers, and return it to the column after cooling. Plants handling ammonia oxidation gas typically provide sufficient cooling to the column by one or the other means so that the strong acid exiting the column is cooler than about 120°F, or even lower depending upon the strength of the nitric acid that is being manufactured.
In contrast to the recovery of nitric acid
from ammonia oxidation gases there has been very little need around the world to recover nitric acid from concentrated NOχ streams such as that described above for the decomposition of aluminum nitrate materials.
Summary of the Invention;
The NOχ recovery process of the present invention comprises contacting NOχ gases containing at most relatively small proportions of inert diluant gases such as N2 in counter-current relation with a cooled 50-60% nitric acid solution in one or more packed columns operating at .about or slightly below atmospheric pressure to remove as nitric acid a major portion, preferably 90% or more, of the originally introduced NOχ values, compressing the residual depleted gases to 2 to 6 or more atmospheres absolute and contacting the compressed gases in counter-current relation with the nitric acid solution in a packed tower to strip substantially all of the remaining nitric acid values from the gas stream.
Detailed Description:
According to the present invention, the reconstitution of such NOχ gases to nitric acid is most efficiently performed as follows:
NOχ gases, produced by thermal decomposition of aluminum nitrate materials and consisting essentially of NOχ, O2, and water vapor and possibly small amounts of N2 from air in-leakage, are partially cooled and absorbed in recirculating cooled, 50 to 60% nitric acid solution from a common receiver tank in one or more packed absorption towers. Nitric acid gas is contacted in a first packed absorption tower operating around atmospheric pressure to 5-50 inches water column negative pressure in counter-current relationship to an amount of cooled nitric acid solution sufficient to
keep the temperature of the acid solution leaving the column at below about 180ºF, the unabsorbed gases exiting the tower are compressed to at least about 20 psig and preferably within a range of about 20 to about 100 psig and contacted in a second, pressurized packed absorption column in counter-current relationship with a quantity of the cooled 50-60% nitric acid solution sufficient to maintain the temperature of the liquor leaving the second column below about 150°F, preferably below about 130°F, and residual gases from the second tower are passed through a small absorber in countercurrent relationship to a flow of a small amount of water to absorb excess HCl gases and then passed to suitable tail gas NOχ recovery or destruction means before venting to the atmosphere.
Before contacting the gases in the said second, pressurized packed absorption column the NOχ gases are blended with sufficient air to provide about 2-10 percent or more O2 in the tail gas. This air may be introduced at any convenient location upstream of the second absorption column and is preferably introduced upstream of the first packed absorption tower.
The nitric acid solution is maintained at about the acid concentration required for extraction, i.e. within the range of about 50 to 60% acid, usually about 54 to 58%, and is supplied from one or more surge tanks, as may be desired, through heat exchangers to the individual packed columns at rates to each column such that the acid solution leaving the column is less than about 180°F in temperature, preferably less than about 150°F. Liquid draining from the towers is collected in the surge tank for recirculation and the excess is drawn off as product acid for use, for instance, for the digestion of alumina from calcined clay for the manufacture of aluminum nitrate in a
process for the recovery of metallurgical grade alumina from clay. More specifically, according to a preferred method, concentrated N0χ gases from aluminum nitrate decomposers are mixed with hot make-up N0χ gases from an NH-,-oxidizer, pass through a waste heat boiler, wherein re-usable heat is extracted, and then blended with vent gases, and with air introduced through a flow control valve that is responsive to an oxygen meter. The mixed gases pass in to an open spray tower where they are counter-currently contacted with acid to remove a portion of the contained heat, water vapor, and N02 and then pass sequentially through one or more packed towers, in which they are counter-currently contacted with acid which has been cooled in a heat exchanger, and then compressed in a compressor to 2 to 6 or more atmospheres absolute pressure before passing through another packed tower in counter-current contact with cooled acid. The vapors are then passed through a bubble cap tower where they are contacted counter- currently with water to absorb HCl values that may be present and the remaining gases pass through an absorber for stripping out any residual N0χ before exhausting to the atmosphere. Nitric acid solution draining from all of the towers is collected in a tank, in which the acid concentration is controlled to below 60%, or preferably below about 58%, by means of the addition of relatively strong acid from the aforesaid acid and heat recovery operations.
The reaction towers are packed absorption columns wherein the packing may be any desired commercially available packing material which preferably has a large void volume per unit of surface area such as is true of Raschig rings. The large void volume of, for instance, Raschig rings minimizes the velocity of flow of the gas through the packing, thereby providing gas residence time for the relativel
slow Reaction 2 to proceed. This reaction time would have to be provided by increasing the height of the tower if packing with a lower void volume were provided. Such rings also simultaneously provide a large gas-liquid contact area which in well known manner facilitates the absorption of NO2 into the liquid and desorption of the reaction product NO from the liquid.
Void volumes for a number of packing materials available are in "Chemical Engineers Handbook" Fifth Edition edited by Perry and Chilton - McGraw-Hill Publishing Company, New York, N.Y.; Section 18: Gas-Liquid Contacts. This section also discusses the relative efficiencies of various packing materials for absorption of gases into liquids and presents methods of estimating absorption rates, heat-transfer rates, pressure drops, etc. Data also may be obtained from packing manufacturers and from other well-known publishing sources.
As mentioned hereinabove, plate-type absorption columns generally are used for absorption of NOχ from gases produced by oxidation of NH3 with air to obtain the maximum possible void volume, and gas residence time wherein Reaction 2 may proceed substantially to completion. For the concentrated gases addressed herein, however, an even more important requirement is the abstraction of sensible heat from the gas phase produced therein by the exothermic Reaction 2, whereby the temperature rise of the gas phase, with the attendant rapid decrease in the rate of Reaction 2, is minimized. Packed towers are much more efficient for the removal of this sensible heat than tray-type towers, and in addition evaporation of water and acid from the myriads of small droplets dispersed in the gas phase further assists in minimizing the gas temperature rise thereby permitting use of much smaller
equipment than would be possible with tray-towers.
The following examples are intended to bette describe and more clearly point out the advantages and preferred manipulative steps of each of the steps of the process of the instant invention.
The following modified technique might be applied in the processes of the following examples as follows:
Concentrated NOχ gases from ANN decomposers are mixed with hot make-up NOχ gases from an NH3- oxidizer, pass through a waste heat boiler, wherein re-usable heat is extracted, and then blended with vent gases and air. The mixed gases pass in to an open spray tower where they are counter-currently contacted with acid to remove a portion of the contained heat, water vapor, and N02 and then pass sequentially through two packed towers, in which they are counter-currently contacted with acid which has been cooled, and then compressed in a compressor to 2 to 6 or more atmospheres absolute pressure before passing through a third packed tower in counter-current contact with cooled acid. The gases are then passed through a bubble cap tower where they are contacted counter- currently with water to absorb HCl values that may be present and the remaining gases pass through a NOχ absorber for stripping out any residual NOχ before exhausting to the atmosphere. Nitric acid solution draining from all four of the towers is collected in a tank in which the acid concentration is controlled to below 60%, or preferably below about 58%, by means of the addition of relatively strong acid.
Example 1
Feed gas having an estimated rate (in pound- mols per hour) and temperature shown in Column 2 of Table 1 is mixed with makeup gas from an atmospheric
pressure NH3-oxidation unit at a rate shown in Column 3, Table 1 and passed through a waste-heat boiler in which heat is extracted and is blended with air from Column 4, Table 1 to produce an assumed column feed gas as given in Column 5, Table 1. To better illustrate the simplicity of the absorption process it is assumed that the gas is cooled only to about 250°F and that no water is condensed in the heat exchanger, although such is not common practice in the nitric-acid-from-ammonia industry. It is also thought that, in many instances, heat exchangers for cooling and dewatering the gas may be more expensive than liquid-acid-to-water heat exchangers for removing the same quantity of heat.
Since the column feed gases will reconstitute to about 64% nitric acid, an unnecessarily-high concentration that would increase unduly the difficulty of absorption and reconstitution, about 191 tons per hour of about 54% nitric acid solution are fed to the product holding tank. Such addition alone maintains the concentration in the product tank at about 56.9%, a satisfactorily low value. In addition about 9.4 tons of dilution water are added to reduce the mean concentration in the tank to about 55% nitric acid.
Example 2
The column feed gas from Example 1 is introduced to a first packed tower, which comprises 160 square feet of internal cross-section area, about 14.3 feet inside diameter, and is packed with 2-inch metal Raschig rings. The tower is fed with about 4565 GPM of acid solution which is cooled to about 100°F and which is distributed over the packing and drains through the packing in counter-current relation to the rising feed gas. The liquid absorbs nitric acid and water (and a little NO2) from the feed gas and drains from the
column at a rate of about 4810 GPM at a temperature of about 175°F. At the gas and liquid rates existing at the base of the packing the pressure drop is about 1.5 inches water column per foot of packing, just below flooding conditions, but the absorption rate of NO2, and particularly H20, is so rapid that the gas volume decreases to about 1/2 of the initial volume within about a foot of effective packing height, whereby the pressure drop is reduced to well below that required for flooding.
At a level in the column corresponding to about 12-1/2 feet of fully-effective packing over 90% of the feed N0χ values have been absorbed and the gas flow rate and composition is that given in Column 2, Table 2. Both reactions (1) and (2) are continuing but at reduced rates.
At a column height equal to about 24 feet of fully-effective packing the gas rate and composition is that given in Column 3, Table 2.
Example 3
The gas from the 12-1/2 ft. effective packing height of Example 2 is compressed to 3.0 atmospheres absolute and fed into a packed absorption column. The packed column has an inside cross-sectional area of 53.6 square feet, inside diameter about 8.26 feet, and is fed with about 1200 GPM of 55% acid cooled to about 114°F which absorbs acid, heat and water vapor from the gas during counter-current contact in the packing so that the liquid draining from the column comprises about 1213 GPM at a temperature of about 130°F. The column is packed with 2-inch Raschig rings.
Because of the high partial pressures of both NO and O2 in the compressed gas, NO is oxidized to NO2 by Reaction 2 at a rate of nearly 5 pound moles NO per hour per cubic foot of void volume, with an
attendant high rate of heat release to the gas. Since the rate of Reaction 2, which is very important in this column, is inhibited by high gas temperatures it is desirable to use a liquid seal of cool acid in the compressor, and to make the compressor to column connection relatively short so that oxidation occurs mainly within the column where the gas is cooled by contact with the liquid and liquid spray.
The quantities of NOχ remaining, including minor amounts of N2O3 and N2O4, and HNO3 vapors, at column heights equivalent to the listed packing height in feet of fully effective packing are given in Table 3.
If the system feed gas contains HCl in excess of the small amounts soluble in 55% nitric acid, the off-gas from the selected effective packing height of the column is passed through a mist eliminator to another column wherein it is contacted in counter- current relation with 200 to 300 pounds per hour of water, as needed to keep the concentration of the weak acid exiting below about 25 wt.% total acid, whereby the HCl and HNO3 vapors are absorbed along with minor amounts of the contained NOχ values. The absorption, as HNO3, of the NOχ values is minimized by limiting the number of trays and the gas residence time to the minimum values required for proper design for absorbing the very-easily-absorbed HCl . It is known to treat the HCl-containing liquid with ozone to convert the HCl to Cl2 gas, which is removed and absorbed in caustic liquor, and return the HCl-free acid to the process.
The tail gas exits the column through a mist eliminator, passing a O2 concentration sensor, to an NOχ stripping unit which is preferably a proprietary Pura Siv N unit manufactured for sale to the industry by Union Carbide Corporation, New York, New York, that is known to strip the N0χ concentration to 50 ppm or
less and permit recycling of the recovered N0χ to the reconstitution system (USP 3,473,893, Hardison).
It is also known to catalytically reduce the N0χ to N2 with ammonia or methane or to absorb the NOχ in nitric acid solutions from which all residual NOx has been stripped by treatment with hot air in a stripping column. Acid offered for commercial sale usually has been bleached, that is, stripped in such manner.
The stripped tail gas is then exhausted to the atmosphere through, if desired, power recovery means well known to the industry.
Example 4.
The gas from the 24 foot effective packing height of Example 2, listed in Column 3 of Table 2, is compressed to 6.0 atmospheres absolute pressure and contacted in a 12.6 square foot inside area, 4 foot inside diameter, column packed with 2 inch Raschig rings and supplied as in Example 3 with about 280 GPM of 55% acid solution at about 104°F which, after absorbing heat, nitric acid and water vapor, exits the column at about 130ºF. The NOχ and HN03 contents of the residual gas at various effective packing heights are listed in Table 4. The gas exiting the column through the mist eliminator is treated as described in Example 3.
Example 5
Examples 2-4 show the use of a single atmospheric-pressure absorption column ahead of the high-pressure column. This example shows the use of a short, large-diameter atmospheric pressure column for removing the bulk of the water from the gases followed by absorption in a taller, smaller-diameter atmospheri pressure column to complete absorption of 90% or more
of the NOχ in the column feed gas (Table 1, Column 5).
The column feed gas (Table 1, Column 5) is absorbed in a first column of 160 square feet cross- section area packed with 6-1/2 feet effective depth of 2 inch Raschig rings supplied with about 4585 GPM of acid liquor cooled to about 100ºF, yielding a liquid effluent of about 4810 GPM at about 162ºF. Residual gas exiting at the top of this column is fed to an atmospheric pressure column which comprises a 7 ft. inside diameter column packed with 2-inch Raschig rings supplied through a sprayer with about 845 GPM of acid cooled to about 100°F.
At a column height corresponding to about 15 feet of effective packing height the gas composition and heat content are essentially the same as those obtained in Example 2 for 12-1/2 feet of effective packing (Table 2, Column 2). Upon comparison to the total volumes of effective packing it is seen that the 2-column combination saves about 400 cubic feet of effective packing volume over the single, large diameter column of Example 2.
Similarly it is found that at an effeccive packing height of about 47 feet in the 7-foot diameter column the gas conditions essentially match those of Table 2, Column 3 for the 24-foot packing height of Example 2. The savings for this variation is about 980 cu. ft. of effective packing volume.