Processing device and processing method for hydrogen-sulphide-containing barren solution

Abstract

Provided are a treatment method for a barren solution, and a treatment device for a barren solution, with which hydrogen sulfide can be efficiently removed from the barren solution. In an aeration tank provided with a vertical-type cylindrical reaction vessel, stirring blades arranged in the reaction vessel, and an annular aeration tube having a large number of air outlets, which is arranged to a bottom part of the reaction vessel, aeration is performed by blowing gas for aeration into the reaction vessel from a large number of air outlets of the aeration tube while stirring a liquid by rotation of the stirring blades.

Claims

1. A treatment method for a barren solution containing hydrogen sulfide, wherein in an aeration tank provided with a vertical-type cylindrical reaction vessel, stirring blades arranged in the reaction vessel, and an annular aeration tube having 10 to 20 air outlets and being arranged to a bottom part of the reaction vessel, hydrogen sulfide is removed from the barren solution in a hydrogen sulfide removal step arranged as a preceding step of a detoxification step by partly adding a slurry after leaching obtained in a leaching step into a barren solution containing the hydrogen sulfide obtained as a process liquid after a sulfurization process in a hydrometallurgy plant for a nickel oxide ore and introducing gas for aeration into the reaction vessel from 10 to 20 air outlets of the aeration tube to perform aeration while stirring a barren solution containing hydrogen sulfide by rotation of the stirring blades.

2. The treatment method for a barren solution containing hydrogen sulfide according to claim 1, wherein the barren solution obtained by removing the hydrogen sulfide is returned to a solid-liquid separation step to reuse as washing water.

3. The treatment method for a barren solution containing hydrogen sulfide according to claim 1, wherein aeration is performed by the aeration tube formed in an annular shape having a diameter size of 70 to 90% of that of the reaction vessel.

4. The treatment method for a barren solution containing hydrogen sulfide according to claim 3, wherein aeration is performed from the air outlets formed in a circular shape having a diameter of 10 to 20 mm.

5. The treatment method for a barren solution containing hydrogen sulfide according to claim 4, wherein aeration is performed via short tube pipes arranged at equal intervals in the aeration tube as the air outlets.

6. The treatment method for a barren solution containing hydrogen sulfide according to claim 5, wherein the gas for aeration is air.

7. A treatment device for a barren solution containing hydrogen sulfide, comprising: an aeration tank provided with a vertical-type cylindrical reaction vessel, stirring blades arranged in the reaction vessel, and an annular aeration tube having 10 to 20 air outlets and being arranged to a bottom part of the reaction vessel, wherein in the aeration tank, hydrogen sulfide is removed from the barren solution in a hydrogen sulfide removal step arranged as a preceding step of a detoxification step by partly adding a slurry after leaching obtained in a leaching step into a barren solution containing the hydrogen sulfide obtained as a process liquid after a sulfurization process in a hydrometallurgy plant for a nickel oxide ore and introducing gas for aeration into the reaction vessel from 10 to 20 air outlets of the aeration tube to perform aeration, while adding a part of slurry after leaching obtained in a leaching step to a barren solution containing the hydrogen sulfide obtained as a process liquid after sulfurization process in a hydrometallurgy plant for a nickel oxide ore and stirring a barren solution containing hydrogen sulfide by rotation of the stirring blades, wherein aeration is performed by the aeration tube formed in an annular shape having a diameter size of 70 to 90% of that of the reaction vessel, aeration is performed from the air outlets formed in a circular shape having a diameter of 10 to 20 mm, and aeration is performed via short tube pipes arranged at equal intervals in the aeration tube as the air outlets.

8. The treatment device for a barren solution containing hydrogen sulfide according to claim 7, wherein the barren solution obtained by removing the hydrogen sulfide is returned to a solid-liquid separation step to reuse as washing water.

9. The treatment device for a barren solution containing hydrogen sulfide according to claim 7, wherein the gas for aeration is air.

Description

BRIEF DESCRIPTION OF THE DRAWINGS

(1) FIG. 1 is a perspective view illustrating essential constitution of a constitution example of a barren solution treatment device to which the present invention is applied, by seeing through the constitution.

(2) FIG. 2 is a process chart of a hydrometallurgy plant for a nickel oxide ore, in which a barren solution treatment device is used.

(3) FIG. 3 is a perspective view illustrating essential constitution of air outlets arranged to an aeration tube in a barren solution treatment device.

(4) FIG. 4 is a process chart of a nickel oxide ore plant by a high pressure acid leach method.

DESCRIPTION OF THE EMBODIMENTS

(5) Hereinafter, a specific embodiment to which the present invention is applied will be described in detail with reference to the drawings.

(6) A treatment method for a barren solution according to the present embodiment is, for example, performed by a barren solution treatment device 100 with the constitution as illustrated in FIG. 1.

(7) The barren solution treatment device 100 is an aeration tank provided with a vertical-type cylindrical reaction vessel 110, stirring blades 120 arranged in the reaction vessel 110, and an annular aeration tube 130 having a large number of air outlets 131 and being arranged to bottom part of the reaction vessel 110. Further, in the vertical-type cylindrical reaction vessel 110, three plates of baffle plates 151 are arranged.

(8) In a treatment method for a barren solution according to the present embodiment, in a vertical-type cylindrical reaction vessel 110, aeration is performed by introducing gas for aeration into the reaction vessel 110 from a large number of air outlets 131 of the aeration tube 130, while stirring a barren solution containing hydrogen sulfide by rotation of stirring blades 120, and the hydrogen sulfide is removed from the barren solution.

(9) For example, in a hydrometallurgy plant for a nickel oxide ore, in a detoxification step as described above, a heavy metal is solidified and removed as a hydroxide by a final neutralization treatment, and a leach residue generated in a solid-liquid separation step and a nickel barren solution generated in a sulfurization step are detoxified and discarded. In this case, in the present embodiment, for example, as shown in a process chart of FIG. 2, a hydrogen sulfide removal step is arranged as a preceding step of a detoxification step, and in the hydrogen sulfide removal step, hydrogen sulfide is removed from a barren solution obtained as a process liquid (solution after sulfurization) after a sulfurization treatment by using the above-described barren solution treatment device 100.

(10) That is, in a reaction tank for removing hydrogen sulfide from a barren solution containing hydrogen sulfide, which is obtained as a process liquid after a sulfurization treatment in a preceding step of a detoxification step, an annular aeration tube 130 having a large number of air outlets 131 is arranged, and the reaction tank is used as the above-described barren solution treatment device 100.

(11) Specifically, in the barren solution treatment device 100 that is the reaction tank, a barren solution containing hydrogen sulfide, which is obtained as a process liquid after a sulfurization treatment, is charged into the vertical-type cylindrical reaction vessel 110, and in the reaction vessel 110, the barren solution containing hydrogen sulfide is stirred by rotation of stirring blades 120. Further, in the reaction vessel 100, for the barren solution, aeration is performed by introducing air as gas for aeration from a large number of air outlets 131 of the annular aeration tube 130, and the sulfur content of the remaining hydrogen sulfide in the barren solution is reduced to sulfur, as a result, the hydrogen sulfide is removed from the barren solution.

(12) In addition, in a hydrometallurgy plant for a nickel oxide ore, into a barren solution containing hydrogen sulfide, which is obtained as a process liquid after a sulfurization treatment, a slurry after leaching, which is obtained in a leaching step, is partly added. Therefore, in the hydrogen sulfide removal step, by the reducing power of Fe.sup.3+contained in the added slurry, the sulfur content of part of the remaining hydrogen sulfide in the barren solution is reduced to sulfur, therefore, hydrogen sulfide can more efficiently be removed from the barren solution.

(13) That is, The barren solution treatment device 100 used for performing a treatment method for a barren solution according to the present embodiment includes an aeration tank provided with a vertical-type cylindrical reaction vessel 110, stirring blades 120 arranged in the reaction vessel 110, and an annular aeration tube 130 having a large number of air outlets 131 and being arranged to the bottom part of the reaction vessel 110, and in the aeration tank, aeration is performed by introducing gas for aeration into the reaction vessel 110 from a large number of air outlets 131 of the aeration tube 130, while stirring a barren solution containing hydrogen sulfide by rotation of stirring blades 120, and the hydrogen sulfide is removed from the barren solution.

(14) As described above, in the barren solution treatment device 100, not only a barren solution containing hydrogen sulfide is stirred by rotation of stirring blades 120 in the reaction vessel, that is, in the aeration tank, but also gas for aeration is blown into the reaction vessel. As a result, the remaining hydrogen sulfide is discharged from the stirred barren solution by aeration, and the residual concentration of the hydrogen sulfide is decreased.

(15) Moreover, in the barren solution treatment device 100, aeration is performed via an annular aeration tube 130 having a large number of air outlets 131 and being arranged to bottom part of the reaction vessel 110, so that bubbles to flow into the reaction vessel 110 are allowed to be split into small bubbles, and the total area of bubbles is tried to be increased. As a result, an abundance of bubbles can be brought into contact with the barren solution containing hydrogen sulfide, which is uniformly stirred in the reaction vessel 110, and a high aeration effect can be obtained. That is, the gas for aeration fed into the reaction vessel 110 becomes in the state of being dispersed on the bottom of the aeration tank from immediately after the feeding, therefore, the aeration can be efficiently performed over the entire barren solution.

(16) In general, the set time of the reaction in a stirring reaction device is usually shorter than the sufficient aeration time by an ordinary aerator. However, according to the barren solution treatment device 100, the retention time in the reaction vessel 100 becomes a prerequisite by the providing of an aeration function in the reaction vessel 110, therefore, even if the sufficient aeration time is not necessarily ensured, the aeration can efficiently be performed as described above, and the hydrogen sulfide can effectively be decreased.

(17) As shown in the process chart of FIG. 2, the barren solution from which hydrogen sulfide has been removed by a barren solution treatment device 100 is returned to the solid-liquid separation step, and can be reused as washing water.

(18) As described above, a hydrogen sulfide removal step is arranged as a preceding step of a detoxification step, and in the hydrogen sulfide removal step, the remaining hydrogen sulfide can effectively be removed by the aeration using the above-described barren solution treatment device 100, therefore, the generation of the hydrogen sulfide gas in a step in which a solution after sulfurization is reused, or in a wastewater treatment step can be suppressed.

(19) The gas for aeration is not particularly limited as long as the gas for aeration is maintained the bubbles in a liquid, that is, not being easily dissolved into a liquid, however, air is preferably used in view of cost.

(20) Further, the shape of the aeration tube is not particularly limited, however, is preferably formed in an annular shape having a diameter size of 70 to 90% of that of the reaction solution 120.

(21) Herein, as to the shape of aeration tube 130, results of the observation of the relationship between the diameter of the aeration tube 130 and the aeration effect, when the diameter of the aeration tube 130 is changed based on the diameter of the reaction vessel 110, are shown in Table 1.

(22) TABLE-US-00001 TABLE 1 Diameter of circular pipe (proportion of diameter to the tank diameter) (%) 50 60 70 80 90 Aeration effect Δ Δ ◯ ◯ ◯

(23) As is apparent from the observation results shown in Table 1, it has been found that a high aeration effect can be obtained by the forming of the aeration tube 130 in the barren solution treatment device 100 in an annular shape having a diameter size of 70 to 90% of that of the reaction vessel 110.

(24) In order to stabilize the flow in the reaction vessel 110 of the barren solution treatment device 100, the air is required to be gone up along the vessel wall. In this respect, the air can efficiently be gone up along the vessel wall by the forming of the aeration tube 130 in the barren solution treatment device 100 in an annular shape having a diameter size of 70 to 90% of that of the reaction vessel 110.

(25) Further, the air outlet 131 formed to the aeration tube is not particularly limited, however, is preferably formed in a circular shape having a diameter of 10 to 20 mm.

(26) Herein, as to the air outlets 131 formed to an aeration tube, results of the observation of the relationship between the bore diameter of the air outlets 131 and the aeration effect, when the bore diameter of the air outlets 131 is changed by the setting of the bore shape as circular, are shown in Table 2.

(27) TABLE-US-00002 TABLE 2 Blowing bore diameter (mm) 5 10 15 20 25 Aeration effect Δ ◯ ◯ ◯ Δ

(28) As is apparent from the observation results shown in Table 2, it has been found that a high aeration effect can be obtained by the forming of the air outlets 131 of the aeration tube 130 in the barren solution treatment device 100 in a circular shape having a diameter of 10 to 20 mm.

(29) It is presumed that there is an optimal bubble size for the density and flow characteristics of the barren solution, and it is considered that if the bubble size is smaller than 10 mm, the rising speed of bubbles in a barren solution is extremely slow, on the other hand, if the bubble size is larger than 20 mm, the rising speed is extremely fast.

(30) Further, the number of the air outlets 131 is not particularly limited, and is preferably appropriately determined depending on the length of the circumference of the aeration tube, however, for example, the number of the air outlets 131 is preferably around 10 outlets, and more preferably 20 outlets.

(31) Herein, as to the number of air outlets 131, results of the observation of the relationship between the number of the air outlets 131 and the aeration effect, when the number of the air outlets 131 is changed, are shown in Table 3.

(32) TABLE-US-00003 TABLE 3 The number of blowing bores 3 5 10 20 Aeration effect Δ Δ ◯ ⊚

(33) As is apparent from the observation results shown in Table 3, it has been found that a high aeration effect can be obtained by the setting of the number of the air outlets 131 of the aeration tube 130 in the barren solution treatment device 100 as 10 outlets, and a much higher aeration effect can be obtained by the forming of 20 outlets.

(34) In the aeration tube 130, when the number of air outlets is increased, the upflow of air becomes weak, and the retention time of the air in an aeration tank is increased, therefore, the aeration efficiency is increased. When the number of air outlets 131 is less than 10, the aeration effect is insufficient, and when the number of air outlets 131 is increased in series, the effect is increased, however, when the number is more than 20, the aeration effect is hardly improved any more.

(35) In addition, the air outlets 131 are not mere pores, when a short pipe (outlet) is attached in the arranged pore, the gas flow is rectified, and the bubble size is stabilized, therefore, this is preferred. Further, the number of the outlets is preferably around 10 to 20.

(36) That is, as to the aeration tube 130, for example, as shown in FIG. 3, when aeration is performed by around 10 to 20 short tube pipes 131A that are arranged at equal intervals as outlets 131, much higher aeration effect can be obtained.

EXAMPLES

(37) Hereinafter, Examples of the present invention will be described, however, the present invention is not limited to the following Examples.

(38) In the present Examples, in a hydrogen sulfide removal step provided as a preceding step of a detoxification step in a hydrometallurgy plant for a nickel oxide ore, a barren solution treatment was performed by using the above-described barren solution treatment device 100.

(39) Table 4 shows results obtained by the measurement of the concentration of the dissolved hydrogen sulfide in a barren solution with or without aeration.

(40) TABLE-US-00004 TABLE 4 Concentration of hydrogen Concentration of hydrogen sulfide gas at an inlet sulfide gas at an outlet (ppm) (ppm) Without aeration 20 15 With aeration 20 5

(41) As is apparent from the measurement results shown in Table 4, when aeration was not performed, the concentration of the dissolved hydrogen sulfide was 20 ppm at an inlet of an aeration tank, and 15 ppm at an outlet of an aeration tank, on the other hand when aeration was performed, the concentration of hydrogen sulfide at an outlet of an aeration tank was largely decreased to 5 ppm, and the dissolved hydrogen sulfide in a barren solution could effectively be decreased by aeration. As described above, it has been found that when a barren solution is treated by using a barren solution treatment device 100, the concentration of the dissolved hydrogen sulfide in the barren solution could effectively be decreased by the aeration.

REFERENCE SYMBOLS

(42) 100, 200 heavy-metal removal device; 110 reaction vessel; 120 stirring blade; 130 aeration tube; 131 air outlet; 131A short tube pipe; 151 baffle plate