JPS5841892B2 - Hiendatsuri Yuhouhou - Google Patents

Hiendatsuri Yuhouhou

Info

Publication number
JPS5841892B2
JPS5841892B2 JP50082527A JP8252775A JPS5841892B2 JP S5841892 B2 JPS5841892 B2 JP S5841892B2 JP 50082527 A JP50082527 A JP 50082527A JP 8252775 A JP8252775 A JP 8252775A JP S5841892 B2 JPS5841892 B2 JP S5841892B2
Authority
JP
Japan
Prior art keywords
gypsum
dust
tower
gas
absorption tower
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
Application number
JP50082527A
Other languages
Japanese (ja)
Other versions
JPS526370A (en
Inventor
正治 天野
忠義 田丸
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
IHI Corp
Original Assignee
IHI Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by IHI Corp filed Critical IHI Corp
Priority to JP50082527A priority Critical patent/JPS5841892B2/en
Publication of JPS526370A publication Critical patent/JPS526370A/en
Publication of JPS5841892B2 publication Critical patent/JPS5841892B2/en
Expired legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、吸収剤に炭酸カルシウム又は消石灰等を使用
する直接石膏回収排煙脱硫設備の小型化及び運転費節減
化を図り得るもので、排煙中にダスト及びフライアッシ
ュ等の不純物を含む場合、除塵塔を設けてダスト又はフ
ライアッシュ等を分離した後、吸収塔にて脱硫して良質
石膏を得るようにしていたのに対し、除塵塔を省略し、
吸収塔のみで脱硫、除塵を行い、石膏回収段階でダスト
、フライアッシュ等と石膏を分離して良質の石膏を得る
ようにした排煙脱硫方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention is capable of downsizing and reducing operating costs of direct gypsum recovery flue gas desulfurization equipment that uses calcium carbonate or slaked lime as an absorbent. When containing impurities such as ash, a dust removal tower was installed to separate the dust or fly ash, and then an absorption tower was used to desulfurize and obtain high quality gypsum.
This invention relates to a flue gas desulfurization method that performs desulfurization and dust removal only in an absorption tower and separates dust, fly ash, etc. from gypsum in the gypsum recovery stage to obtain high-quality gypsum.

従来の直接石膏回収排煙脱硫設備は、第1図にそのフロ
ーチャートを示す如く、ガス発生源aよりの排ガスは、
排ガスファンbで誘引昇圧されて冷却除塵塔Cへ入り、
ガス冷却を行うと共に排ガス中のダストを分離せしめら
れ、液中に捕集されたダストはフィルターgを介してそ
れのみ分離して取出され、又冷却除塵塔Cを出たガスは
吸収塔dに入り脱硫される。
In the conventional direct gypsum recovery flue gas desulfurization equipment, as shown in the flowchart in Figure 1, the flue gas from gas generation source a is
The exhaust gas fan B increases the pressure and enters the cooling dust removal tower C.
The gas is cooled and the dust in the exhaust gas is separated, and the dust collected in the liquid is separated and taken out through a filter g, and the gas leaving the cooling dust removal tower C is sent to an absorption tower d. It is desulfurized.

脱硫後のガスは、熱風発生装置eからのガスと混合され
煙突fより大気へ放出される一方、吸収塔d内の液は吸
収剤と硫黄酸化物が反応してできた亜硫酸カルシウム、
硫酸カルシウムのスラリー液となっており、そのスラリ
ー液の一部が酸化塔りへ送られ、酸化塔りでは亜硫酸カ
ルシウムが酸化されて石膏スラリー液になる。
The desulfurized gas is mixed with the gas from the hot air generator e and released into the atmosphere from the chimney f, while the liquid in the absorption tower d contains calcium sulfite, which is produced by the reaction between the absorbent and sulfur oxide,
It is a slurry liquid of calcium sulfate, and a part of the slurry liquid is sent to the oxidation tower, where the calcium sulfite is oxidized and becomes a gypsum slurry liquid.

石膏スラリー液は遠心分離機iへ送られて石膏とr液に
分離され、f液は吸収塔dヘフィードバックされて吸収
液として再使用される一方、遠心分離機iで分離された
石膏jは石膏ボードやセメント等に使用される。
The gypsum slurry liquid is sent to the centrifuge i and separated into gypsum and the r liquid, and the f liquid is fed back to the absorption tower d and reused as an absorption liquid, while the gypsum j separated by the centrifuge i is Used for plasterboard, cement, etc.

上記従来設備は、ガス中のダスト及びフライアッシュを
除塵塔Cで捕集して良質の石膏を得るための方法である
が、ガス中の煤煙濃度は捕集した液中の濃度と比較して
極めて低いため、除塵塔Cを設けるよりも吸収塔d内で
脱硫除塵を行い液側もしくは回収石膏から煤煙を分離す
る方法に比べ除塵塔C等の装置コストが高くなり、除塵
塔Cの圧力損失により排ガスファンbの運転費が高くな
るという欠点を有し、又遠心分離機1で分離した石膏含
水率は10%程度もあり、従って重量が重く運搬コスト
が高くなり且つ取扱時付着等が起って非常に作業に手間
がかかる、等の問題点を有していた。
The above conventional equipment is a method for obtaining high-quality gypsum by collecting dust and fly ash in the gas in the dust removal tower C, but the soot concentration in the gas is higher than that in the collected liquid. Since the dust removal tower C is extremely low, the cost of equipment such as the dust removal tower C is higher compared to the method of desulfurizing dust removal in the absorption tower d and separating soot from the liquid side or recovered gypsum rather than installing the dust removal tower C, and the pressure loss of the dust removal tower C. The gypsum separated by the centrifuge 1 has a moisture content of about 10%, which increases the weight and transportation cost, and also causes adhesion during handling. However, there were problems such as the fact that the process was extremely time-consuming.

本発明は上記従来方式の有していた問題点を解決し得る
もので、排ガスを吸収塔に導いて該吸収塔にて吸収脱硫
及び除塵を同時に行L・、吸収塔内水溶液を酸化塔に導
いて石膏の結晶粗大化を行わしめた後、遠心分離機に導
いて脱液し、回収したダスト及びフライアッシュの混入
する石膏を、乾燥後、粒度と比重の違いを利用して分級
することにより高純度の石膏として取り出すことを特徴
とする排煙脱硫方法に係るものである。
The present invention can solve the above-mentioned problems of the conventional system.The exhaust gas is guided to the absorption tower, where absorption and desulfurization and dust removal are simultaneously carried out.The aqueous solution in the absorption tower is transferred to the oxidation tower. After coarsening the gypsum crystals, the gypsum is introduced into a centrifuge to remove liquid, and the gypsum mixed with the collected dust and fly ash is classified after drying using differences in particle size and specific gravity. This relates to a flue gas desulfurization method characterized by extracting high-purity gypsum.

以下図面を参照しつつ本発明の詳細な説明する。The present invention will be described in detail below with reference to the drawings.

第2図は本発明の一例を示すフローチャートであり、図
中1はガス発生源、2は排ガスファン、3は吸収塔、4
は熱風発生装置、5は煙突、6は酸化塔、γは遠心分離
機、8は乾燥機、9は分級機、10は集塵機、11は排
気ファン、12は補給水、13は吸収剤、14は石膏、
15はフライアッシュ及びダストを示す。
FIG. 2 is a flowchart showing an example of the present invention, in which 1 is a gas generation source, 2 is an exhaust gas fan, 3 is an absorption tower, and 4 is a flowchart showing an example of the present invention.
is a hot air generator, 5 is a chimney, 6 is an oxidation tower, γ is a centrifugal separator, 8 is a dryer, 9 is a classifier, 10 is a dust collector, 11 is an exhaust fan, 12 is makeup water, 13 is an absorbent, 14 is plaster,
15 indicates fly ash and dust.

ガス発生源1よりの排ガスは、排ガスファン2で誘引昇
圧されて吸収塔3に入り、ガスの冷却、除塵及び脱硫が
行われ、熱風発生装置4からの熱風と混合昇温されて煙
突5より大気へ放出される3一方吸収剤13と補給水1
2が吸収塔3に入れられるため吸収塔3内の液は亜硫酸
カルシウム、硫酸カルシウム、ダスト等を含む水溶液と
なり、更に酸化塔6へ送られて亜硫酸カルシウムが硫酸
カルシウムとなって石膏とダスト等の含有水溶液になる
The exhaust gas from the gas generation source 1 is induced to be pressurized by the exhaust gas fan 2 and enters the absorption tower 3, where the gas is cooled, dust removed, and desulfurized, mixed with hot air from the hot air generator 4, heated, and sent out from the chimney 5. 3 released into the atmosphere, 1 absorbent 13 and make-up water 1
2 is put into the absorption tower 3, so the liquid in the absorption tower 3 becomes an aqueous solution containing calcium sulfite, calcium sulfate, dust, etc., and is further sent to the oxidation tower 6, where the calcium sulfite turns into calcium sulfate and contains gypsum, dust, etc. becomes a containing aqueous solution.

更に溶液は遠心分離機7に導かれて石膏、ダスト等の固
形分とr液に分離され、沢液は吸収塔3ヘフイードバツ
クされて再使用される一方、分離された石膏、ダスト等
の固形分は約10%程度の水分を含んでいるので乾燥機
8で乾燥する。
The solution is then led to a centrifuge 7 where it is separated into solids such as gypsum and dust and r-liquid.The liquid is fed back to the absorption tower 3 and reused, while the separated solids such as gypsum and dust are separated. Since it contains about 10% water, it is dried in the dryer 8.

乾燥後の固形分は乾燥機8の排ガス又は空気で分級機9
へ送り粒径と比重の違いを利用して分級する。
The solid content after drying is classified by a classifier 9 using exhaust gas or air from the dryer 8.
The particles are classified using differences in particle size and specific gravity.

固形分中石膏14は酸化塔6で結晶粗大化を行わせてい
るので粒子が50〜100μ(ミクロン)であり比較的
大きく、一方ダスト等は1μ〜20μ程度で比較的小さ
いため、分級機9において石膏14が固形分として分離
回収され、又分級機9出ロガスは集塵機10でダスト及
びフライアッシュ15が分離されて排気ファン11より
大気へ放出される。
Since the gypsum 14 in the solid content is coarsened in the oxidation tower 6, the particles are relatively large with a size of 50 to 100μ (microns), while dust etc. are relatively small with a size of about 1μ to 20μ, so the particles are coarsened in the oxidation tower 6. The gypsum 14 is separated and recovered as a solid content, and the log gas from the classifier 9 is separated into dust and fly ash 15 by the dust collector 10 and discharged into the atmosphere from the exhaust fan 11.

乾燥機8に使う刃口熱源としては、重油、ガスを別途に
燃焼させたり、スチームを使用することの他に排ガスフ
ァン2のあとのガスや熱風発生装置4よりのガスやガス
発生源がボイラの場合エアーヒーター後の空気を使用す
れは燃料の節減や廃熱の利用ができ、又、乾燥機8では
通常100℃以上になるため、遠心分離後の固形分が含
水していても略零近くにすることができ、輸送重量が1
0%程度軽減され且つ石膏の機器への付着がなくなるの
で取扱いが容易となり、更に石膏を石膏ボードやセグメ
ントに使用する場合は焼成する必要があるが含有水分が
少ないため焼成用燃料の節約が図れる。
As the heat source for the dryer 8, heavy oil or gas may be separately combusted, steam may be used, the gas after the exhaust gas fan 2, the gas from the hot air generator 4, or the gas generation source may be a boiler. In this case, using the air after the air heater can save fuel and utilize waste heat, and since the temperature in the dryer 8 is usually over 100°C, even if the solid content after centrifugation contains water, it is almost zero. Can be placed nearby and transport weight is 1
It is reduced by about 0% and the plaster does not stick to equipment, making it easier to handle.Furthermore, when using plaster for plasterboard or segments, it must be fired, but since the moisture content is low, fuel for firing can be saved. .

尚、本発明は上記実施例にのみ限定されるものではなく
、本発明の要旨を逸脱しない範囲内において種々変更を
刃口え得るものである。
It should be noted that the present invention is not limited to the above-mentioned embodiments, and various changes can be made without departing from the gist of the present invention.

上述した本発明の排煙脱硫方法によれば (1)除塵塔などが不要になり装置がコンパクト化して
低価格となる、 (ii)運転費が低減される、 (iii) 乾燥機を使用するため付着水が零に近く
なり石膏の重量が軽減し且つ付着などがなくなって輸送
、取扱いが容易になる、 (1ψ 石膏焼成燃料が節約できる、 〜)吸収塔においで、除塵作用と脱硫作用を同時に行わ
せ、且つ酸化塔に導いて石膏の結晶粗大化を行わせた後
、脱水、乾燥することにより、ダスト及びフライアッシ
ュが混入する石膏を、粒度と比重の違いを利用した簡単
な分級手段によって分級することを可能にして高純度の
石膏を取り出せる。
According to the above-described flue gas desulfurization method of the present invention, (1) a dust removal tower etc. are not required, making the device more compact and lower in price, (ii) operating costs are reduced, and (iii) a dryer is used. Therefore, the amount of adhering water is close to zero, the weight of the gypsum is reduced, and there is no adhesion, making transportation and handling easier. At the same time, the gypsum is guided to an oxidation tower to coarsen its crystals, and then dehydrated and dried. This is a simple means of classifying gypsum mixed with dust and fly ash by utilizing the difference in particle size and specific gravity. It is possible to extract high-purity gypsum by classifying the gypsum.

等、種々の優れた効果を発揮する。etc., exhibits various excellent effects.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は従来の直接石膏回収排煙脱硫設備のフローチャ
ート、第2図は本発明の実施例を示すフローチャートで
ある。 1はガス発生源、2は排ガスファン、3は吸収塔、6は
酸化塔、γは遠心分離機、8は乾燥機、9は分級機、1
0は集塵機。
FIG. 1 is a flowchart of a conventional direct gypsum recovery flue gas desulfurization equipment, and FIG. 2 is a flowchart showing an embodiment of the present invention. 1 is a gas generation source, 2 is an exhaust gas fan, 3 is an absorption tower, 6 is an oxidation tower, γ is a centrifugal separator, 8 is a dryer, 9 is a classifier, 1
0 is a dust collector.

Claims (1)

【特許請求の範囲】[Claims] 1 排ガスを吸収塔に導いて該吸収塔にて吸収脱硫及び
除塵を同時に行い、吸収塔内水溶液を酸化塔に導いて石
膏の結晶粗大化を行わしめた後、遠心分離機に導いて脱
液し、回収したダスト及びフライアッシュの混入する石
膏を、乾燥後、粒度と比重の違いを利用して分級するこ
とにより高純度の石膏として取り出すことを特徴とする
排煙脱硫方法。
1. The exhaust gas is led to an absorption tower where absorption and desulfurization and dust removal are performed at the same time, and the aqueous solution in the absorption tower is led to an oxidation tower to coarsen the crystals of gypsum, and then led to a centrifugal separator for deliquification. This flue gas desulfurization method is characterized in that the collected gypsum mixed with dust and fly ash is dried and then classified using differences in particle size and specific gravity to extract high-purity gypsum.
JP50082527A 1975-07-04 1975-07-04 Hiendatsuri Yuhouhou Expired JPS5841892B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP50082527A JPS5841892B2 (en) 1975-07-04 1975-07-04 Hiendatsuri Yuhouhou

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP50082527A JPS5841892B2 (en) 1975-07-04 1975-07-04 Hiendatsuri Yuhouhou

Publications (2)

Publication Number Publication Date
JPS526370A JPS526370A (en) 1977-01-18
JPS5841892B2 true JPS5841892B2 (en) 1983-09-16

Family

ID=13776981

Family Applications (1)

Application Number Title Priority Date Filing Date
JP50082527A Expired JPS5841892B2 (en) 1975-07-04 1975-07-04 Hiendatsuri Yuhouhou

Country Status (1)

Country Link
JP (1) JPS5841892B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0324574Y2 (en) * 1985-04-25 1991-05-29
CN101844021A (en) * 2010-01-15 2010-09-29 梁鑫 New process for closed absorbing, cooling, desulfurizing and purifying high-temperature waste gas

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS49110574A (en) * 1973-02-24 1974-10-21

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS49110574A (en) * 1973-02-24 1974-10-21

Also Published As

Publication number Publication date
JPS526370A (en) 1977-01-18

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