Denitrator
10478774 ยท 2019-11-19
Assignee
Inventors
- Keiichi Nakagawa (Tokyo, JP)
- Mikiya Sakurai (Tokyo, JP)
- Kiyoto Itakura (Tokyo, JP)
- Hitoshi Tokunaga (Tokyo, JP)
- Naoya Okuzumi (Tokyo, JP)
- Hirokazu Tsutsumi (Tokyo, JP)
Cpc classification
F23J15/00
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
B01D2257/404
PERFORMING OPERATIONS; TRANSPORTING
B01D53/76
PERFORMING OPERATIONS; TRANSPORTING
F23J15/006
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F23J15/003
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
International classification
B01D53/76
PERFORMING OPERATIONS; TRANSPORTING
Abstract
A denitrator removes nitrogen oxide in a flue gas generated from a combustion furnace by injecting a reducing agent into the flue gas. The denitrator includes a housing disposed above the combustion furnace. The housing includes a discharge port for the flue gas at one end of the housing. A cross-sectional area of flow of the flue gas gradually increases toward the discharge port. The housing gathers and guides the flue gas to the discharge port. The denitrator injects the reducing agent in another end of the housing.
Claims
1. A denitrator for removing nitrogen oxide in flue gas generated from a combustion furnace by injecting a reducing agent into the flue gas, the denitrator comprising: a housing disposed above the combustion furnace, wherein the housing comprises a discharge port for the flue gas at one end of the housing, wherein a cross-sectional area of flow of the flue gas gradually increases toward the discharge port, wherein the housing gathers and guides the flue gas to the discharge port, wherein the denitrator injects the reducing agent into another end of the housing, and wherein the housing comprises a ceiling that is inclined downward from the one end toward the another end.
2. The denitrator according to claim 1, wherein the reducing agent comprises ammonia gas, and wherein the denitrator injects the ammonia gas into the flue gas, and wherein, when the flue gas has a temperature of at least 1000 C., the ammonia gas relative to a flow rate of the flue gas is not more than 0.1 vol %, or in a range of 0.01 to 0.06 vol %.
3. The denitrator according to claim 2, wherein the denitrator injects the ammonia gas into the flue gas in a first region on the another end that accounts for at most 50% of the flue gas in the housing, and at least 50% of the ammonia gas is injected in a second region on the another end that accounts for at most 30% of the flue gas in the housing.
4. The denitrator according to claim 3, wherein a flow velocity of injecting the ammonia gas is in a range from 100 to 2000 Nm/s.
5. The denitrator according to claim 4, wherein the denitrator injects nitrogen simultaneously with and from the same position as the ammonia gas.
6. The denitrator according to claim 5, wherein an amount of supply of the nitrogen is 0.1 to 5 times as large as an amount of supply of the ammonia gas.
Description
BRIEF DESCRIPTION OF DRAWINGS
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DETAILED DESCRIPTION
(6) Hereinafter, a denitrator according to embodiments of the present invention will now be described in detail with reference to
(7) In a denitrator 1 in accordance with one or more embodiments, ammonia gas is used as a reducing agent. Nitrogen oxide in flue gas generated in combustion furnaces 2 is removed by injecting the ammonia gas.
(8) The denitrator 1 includes a pair of combustion furnaces 2, 2 which are placed at an appropriate distance therebetween; and a housing 3 which is positioned above these combustion furnaces and covers the tops thereof. Each of the combustion furnaces 2 includes a plurality of burners 2c arranged in two or more lines from one end 2a to another end 2b of the combustion furnace (see
(9) The housing 3 includes a discharge port 5 at one end 3a of the housing, which discharges flue gas from the combustion furnaces 2 to a heat exchanger 4. In addition, as schematically shown in
(10) Due to the aforementioned shape of the housing 3, the flue gas discharged from the combustion furnaces 2, 2 is gathered by the housing 3 located thereabove and is guided to the discharge port 5 along the inclination of the ceiling 3d, as indicated with arrows in
(11) Nozzles 6 for injecting and supplying the ammonia gas into the flue gas are arranged on the shoulder parts 3b, 3b on the two sides near the other end 3e of the housing 3. For ease of description hereinbelow, the housing 3 will be divided evenly into six regions from the one end 3a to the other end 3e and the boundaries thereof will be denoted by A, B, C, D, E, F, and G, respectively (see
(12) Positions of the nozzles 6 to inject the ammonia gas are located in a region on a side of the other end 3e (i.e., from boundaries D to G in
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(14) An operation of the denitrator 1 in accordance with one or more embodiments will be described.
(15) As indicated by arrows in
(16) More specifically, the amount of the flue gas is low on the upstream side of the flue gas in the denitrator 1. Accordingly, even when the proportion of the ammonia gas relative to the entire amount of the flue gas is small, the proportion of the ammonia gas becomes higher in the region on the upstream side so that the effect of cooling the flue gas on the upstream side can be obtained. In the meantime, a flow velocity of the flue gas is low on the upstream side and the ammonia gas supplied thereto is not mixed soon. Accordingly, the ammonia gas spreads into the flue gas in the housing 3 along with the flow of the ammonia gas to the downstream side. Thus, the group of low-temperature ammonia gas reduces the temperature of the flue gas in a wide range so that the ammonia gas enables the reduction of the NOx in the flue gas to progress efficiently. According to the method using this device, denitration efficiency is around 15% (10% to 20%).
(17) Furthermore, in one or more embodiments, when the flue gas has a temperature of 1000 C. or above, the ammonia gas is injected into the flue gas such that the ammonia gas relative to a flow rate of the flue gas is up to 0.1 vol % at a maximum. A flow velocity of injecting the ammonia gas to be supplied is set in a range from 100 to 2000 Nm/s or preferably in a range from 300 to 1000 Nm/s. In this way, it is possible to achieve the partial cooling effect of the flue gas and to obtain the denitration effect at high efficiency.
(18) Here, if the injection rate of the ammonia gas into the flue gas is equal to or above 2000 Nm/s, the ammonia gas spreads in a wide range and fails to achieve the partial cooling effect and the temperature remains high. As a consequence, the denitration effect is hardly obtained and the NOx is rather increased. On the other hand, if the injection rate of the ammonia gas into the flue gas is equal to or below 100 Nm/s, the concentration of the ammonia gas becomes locally high, whereby the NOx reduction reaction is limited and a sufficient denitration efficiency is not achieved.
(19) Meanwhile, nitrogen may be supplied simultaneously with the supply of the ammonia gas and from the same position as the nozzles 6 for the ammonia gas. In this way, nitrogen can suppress a rise in temperature of the group of the ammonia gas, and a concentration of oxygen around the group of the ammonia gas is reduced at the same time. Thus, it is possible to inhibit this ammonia from turning into NOx. Here, the amount of supply of nitrogen is set preferably in a range from 0.1 to 5 times or more preferably in a range from 0.5 to 2 times as large as the amount of supply of the ammonia gas.
(20) It is to be noted that no effect is achieved if the amount of supply of nitrogen is 0.1 times or less than the amount of supply of ammonia. On the other hand, if this ratio is 5 times or more, the chance of contact with the NOx is reduced and no reaction will take place. In addition, the latter case requires a large amount of nitrogen and is therefore uneconomical.
(21) Examples showing a NOx removal effect of by this denitrator 1 will be described with reference to
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(25) In one or more embodiments shown in
(26) In one or more of the above-described embodiments, the denitrator is applied to the combustion furnaces for heating the reaction tubes. However, the present invention is not limited to this configuration. One or more embodiments of the present invention are also applicable to any combustion furnace as long as it is a combustion furnace such as a garbage incinerator, which requires the NOx reduction. In short, such a combustion furnace only needs to be configured to be able to supply the ammonia gas to a far side of the housing from the discharge port of the flue gas.
REFERENCE SYMBOL LIST
(27) 1 denitrator 2 combustion furnace 2a one end 2b another end 2c burner 3 housing 3a one end 3b shoulder part 3c central part 3d ceiling 3e other end 4 heat exchanger 5 discharge port 6 nozzle
(28) Although the disclosure has been described with respect to only a limited number of embodiments, those skilled in the art, having benefit of this disclosure, will appreciate that various other embodiments may be devised without departing from the scope of the present invention. Accordingly, the scope of the invention should be limited only by the attached claims.