JPS6043198B2 - Neutralization and solidification treatment method for waste sulfuric acid - Google Patents

Neutralization and solidification treatment method for waste sulfuric acid

Info

Publication number
JPS6043198B2
JPS6043198B2 JP2387577A JP2387577A JPS6043198B2 JP S6043198 B2 JPS6043198 B2 JP S6043198B2 JP 2387577 A JP2387577 A JP 2387577A JP 2387577 A JP2387577 A JP 2387577A JP S6043198 B2 JPS6043198 B2 JP S6043198B2
Authority
JP
Japan
Prior art keywords
sulfuric acid
neutralization
waste sulfuric
reaction
neutralization reaction
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
JP2387577A
Other languages
Japanese (ja)
Other versions
JPS53108877A (en
Inventor
隆 秋山
泰樹 橋本
広満 浅野
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.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
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 Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP2387577A priority Critical patent/JPS6043198B2/en
Publication of JPS53108877A publication Critical patent/JPS53108877A/en
Publication of JPS6043198B2 publication Critical patent/JPS6043198B2/en
Expired legal-status Critical Current

Links

Landscapes

  • Incineration Of Waste (AREA)

Description

【発明の詳細な説明】 を−ユ”i−)卜陸ヨー(コIレ“IL゛−にブhn
−f!廿仕に関するものにして、更に詳細には、石灰燃
焼火力発電所の活性炭法の如き脱硫過程て硫酸を生成す
る脱硫装置を採用するものにおいて、生成した硫酸を廃
硫酸としてフライアッシュを用いて中和して処理する方
法に関するものである。
[Detailed description of the invention]
-f! More specifically, in a lime-burning thermal power plant that uses a desulfurization device that generates sulfuric acid during the desulfurization process, such as the activated carbon method, the generated sulfuric acid is used as waste sulfuric acid and is used for intermediate treatment using fly ash. This relates to a method of summing and processing.

排煙脱硫装置における脱硫生成物たる廃硫酸は石膏とし
て回収する方法か最も多く採用されており、脱硫過程て
硫酸を生成する活性炭法の場合も回収硫酸は工場のアル
カリ廃液の中和用や肥料用として用いられるものの、そ
れ等に対する需要量としてはあまり多くを期待すること
はできなく、また希薄硫酸では輸送、貯蔵の点で問題が
あるため、石灰石スラリ等を用いて中和して石膏にして
回収することが行われている。
The most commonly used method is to recover waste sulfuric acid, which is a desulfurization product in flue gas desulfurization equipment, as gypsum.In the case of the activated carbon method, which generates sulfuric acid during the desulfurization process, the recovered sulfuric acid can be used to neutralize alkaline wastewater from factories or as fertilizer. Although it is used for various purposes, the demand for it cannot be expected to be very large, and dilute sulfuric acid has problems in transportation and storage, so it is neutralized using limestone slurry, etc. and turned into gypsum. It is being collected by

この場合、中和反応を溶液中で行うため、大容量の反応
槽や固液分離のための分離器等を必要とし、更に分離排
液の無害化処理を必要とするのでその設備をも必要とす
るため大きな設備を必要とする欠点のあるものである。
ノ 一方フライアッシュは、セメント用混和剤等として
一部は有効利用されているものの、処理費を出費して専
門業者に廃棄処理を依託しているのが現状であり、経済
的問題点を含んているものである。
In this case, since the neutralization reaction is carried out in a solution, a large-capacity reaction tank and a separator for solid-liquid separation are required, and furthermore, the separated waste liquid needs to be detoxified, so such equipment is also required. This method has the disadvantage of requiring large equipment.
On the other hand, although some fly ash is effectively used as an admixture for cement, the current situation is that the disposal of fly ash is outsourced to specialized companies at the expense of processing fees, which poses economic problems. It is something that

7 本発明は以上に述べた如き石炭燃焼炉における欠点
および問題点を解決するためになされたものである。
7 The present invention has been made in order to solve the drawbacks and problems in coal combustion furnaces as described above.

本発明によれば、これらの廃硫酸とフライアッシュとを
混合して中和反応せしめて処理する際、中和反応前の混
合物中の水分を調整することにより中和反応後の生成物
が実質的に固化物となるようにできるものである。
According to the present invention, when these waste sulfuric acid and fly ash are mixed and treated to undergo a neutralization reaction, by adjusting the water content in the mixture before the neutralization reaction, the product after the neutralization reaction is substantially reduced. It can be made into a solidified product.

従つて、極めて簡単に廃硫酸とフライアッシュとを同時
に、やつかいな廃液を生ずることなく処理できるもので
、大きな効果のあるものである。このような本発明の基
礎は下記の通りである。
Therefore, waste sulfuric acid and fly ash can be treated at the same time extremely easily, without producing any complicated waste liquid, and this is highly effective. The basis of the present invention is as follows.

本発明者等の検討によれば、フライアッシュ中には、C
a,.Na..M?亭のアルカリ成分が含まれており、
石炭の炭種によつては、これらの含有量が相当多く、し
かも水和硬化性の鉱物質として存在するため、これを硫
酸を用いて中和する場合、硫酸濃度を適当に選ぶか、あ
るいは添加水量の調節等により、中和反応前混合物中の
水分量を、中和反応時における蒸発気化する水分、反応
生成物中の結晶水、反応生成固化物表面の水分の合計量
となる如く調整して、反応生成物全体を固化物とすると
きは、廃硫酸をフライアッシュと同時に処理できると共
に、廃液を全く生せしめることがないので、極めて有効
である。以上において、硫酸の濃度を調節する場合は、
フライアッシュの成分に,よつて異なるが、排煙回収硫
酸の濃度を20乃至60%にすればよいことが確かめら
れた。また、このような中和反応においては、上記の如
く硫酸濃度は比較的高いものである故、反応時間が短か
く、この間、相変化は混合、流動、固化ζという状態を
たどるため、中和反応を攪拌翼を備えた反応器内て行わ
しめることは有効であることが確認された。
According to the study by the present inventors, fly ash contains C.
a,. Na. .. M? Contains alkaline components of Tei,
Depending on the type of coal, the content of these substances is quite high, and they exist as hydration hardening minerals, so when neutralizing this with sulfuric acid, the sulfuric acid concentration must be selected appropriately, or By adjusting the amount of water added, etc., the amount of water in the mixture before neutralization reaction is adjusted to the total amount of water that evaporates during the neutralization reaction, water of crystallization in the reaction product, and water on the surface of the solidified reaction product. When the entire reaction product is solidified, waste sulfuric acid can be treated at the same time as fly ash, and no waste liquid is produced, which is extremely effective. In the above, when adjusting the concentration of sulfuric acid,
It was confirmed that the concentration of the flue gas recovered sulfuric acid should be set at 20 to 60%, although this differs depending on the components of the fly ash. In addition, in such a neutralization reaction, since the sulfuric acid concentration is relatively high as mentioned above, the reaction time is short, and during this period, the phase changes follow the states of mixing, fluidization, and solidification ζ, so the neutralization It has been confirmed that it is effective to carry out the reaction in a reactor equipped with a stirring blade.

以下に本発明を実施例につき、系統図を参照して説明す
る。
The present invention will be described below with reference to embodiments and system diagrams.

c実施例1本実施
例に用いたフライアッシュの主要化学成分は第1表に示
す如きものである。
c Example 1 The main chemical components of the fly ash used in this example are as shown in Table 1.

4本実施例
においては、第1図の統系図に示す如く、ボイラ1より
出た排出ガスは集じん器2、硫酸濃縮装置3を経て排ガ
ス脱硫装置4に入り、更に煙突5へ導かれる。
4 In this embodiment, as shown in the system diagram of FIG. 1, exhaust gas discharged from a boiler 1 passes through a dust collector 2 and a sulfuric acid concentrator 3, enters an exhaust gas desulfurization device 4, and is further led to a chimney 5.

硫酸濃縮装置3は排煙脱硫装置4て生成される希硫酸を
排ガスの顕熱で濃縮するもので、濃縮された硫酸は濃縮
硫酸タンク6に貯えられる。
The sulfuric acid concentrator 3 condenses dilute sulfuric acid produced by the flue gas desulfurizer 4 using the sensible heat of the exhaust gas, and the concentrated sulfuric acid is stored in a concentrated sulfuric acid tank 6.

この場合、硫酸濃縮装置3における濃縮の程度は、後に
説明する第2表の中和反応条件における硫酸濃度が適用
される。タンク6の濃縮硫酸は硫酸供給ポンプ7により
中和反応器11内へ供給される。その供給量は後に説明
する第2表の中和反応条件における硫酸量が適用される
。フライアッシュの方は、集じん器2で捕集され、フラ
イアッシュホッパ8、定量フィーダ9、移送フィーダ1
0を経由して中和反応器11内へ導かれる。
In this case, the degree of concentration in the sulfuric acid concentrator 3 is determined by the sulfuric acid concentration under the neutralization reaction conditions in Table 2, which will be explained later. Concentrated sulfuric acid in tank 6 is supplied into neutralization reactor 11 by sulfuric acid supply pump 7 . As for its supply amount, the amount of sulfuric acid under the neutralization reaction conditions in Table 2, which will be explained later, is applied. Fly ash is collected by a dust collector 2, and sent to a fly ash hopper 8, a quantitative feeder 9, and a transfer feeder 1.
0 into the neutralization reactor 11.

このようにして中和反応器11内には、硫酸とフライア
ッシュとが供給されて中和反応処理が行われることとな
るのであるが、この中和反応における反応条件は第2表
に示される条件が満されるようにするものてある。
In this way, sulfuric acid and fly ash are supplied into the neutralization reactor 11, and a neutralization reaction process is performed.The reaction conditions for this neutralization reaction are shown in Table 2. There are things that ensure that the conditions are met.

即ち、上記における硫酸濃度の調整と中和反応器11内
の供給量は第2表の反応条件に適合するようにするもの
である。中和反応器11は、本発明の処理における反応
を効果的に行わしめるための攪拌翼を備えた構造のもの
である。中和反応器11内に供給された硫酸とフライア
ッシュの混合物は攪拌翼によつて攪拌されて中和反応処
理されて、反応器11の下から排出された生成物は実質
的に固化物であつた。この固化物はコンベア12により
貯蔵場へ運ばれ固化物13として貯蔵される。以上のよ
うにして、本発明によれば、廃硫酸はフライアッシュに
より、廃液の発生を伴うことなく固形物化されて処理さ
れることができるので、廃硫酸とフライアッシュの処理
が同時になされることとなる。
That is, the above-described adjustment of the sulfuric acid concentration and the amount of sulfuric acid supplied into the neutralization reactor 11 are made to conform to the reaction conditions shown in Table 2. The neutralization reactor 11 has a structure equipped with stirring blades for effectively carrying out the reaction in the treatment of the present invention. The mixture of sulfuric acid and fly ash supplied into the neutralization reactor 11 is stirred by a stirring blade and subjected to a neutralization reaction treatment, and the product discharged from the bottom of the reactor 11 is substantially solidified. It was hot. This solidified material is transported to a storage area by a conveyor 12 and stored as a solidified material 13. As described above, according to the present invention, waste sulfuric acid can be solidified and processed by fly ash without generating waste liquid, so waste sulfuric acid and fly ash can be processed at the same time. becomes.

実施例2 この実施例は、第2図の系統図に示す如きもので、上記
の実施例1と異なる点は、中和反応器11内に供給され
るフライアッシュには、石灰石、石灰の如きアルカリが
添加剤として添加される点である。
Example 2 This example is as shown in the system diagram in FIG. 2, and is different from Example 1 described above in that the fly ash supplied into the neutralization reactor 11 contains limestone, The point is that alkali is added as an additive.

添加剤は、添加剤ホッパ8″、添加剤定量フィーダ9″
により移送フィーダ10により、フライアッシュに添加
されて中和反応器11内に供給されるものである。その
他の操作に関して実施例1と全く同様である。
For additives, additive hopper 8″, additive quantitative feeder 9″
The fly ash is added to the fly ash and supplied into the neutralization reactor 11 by the transfer feeder 10. Other operations are completely the same as in Example 1.

この実施例はフライアッシュ中のアルカリ分が少ない場
合に効果のあるものである。
This embodiment is effective when the alkali content in fly ash is low.

以上に実施例と共に説明したように、本発明によれば、
石炭燃焼火力発電所のフライアッシュと排煙脱硫装置副
生硫酸の無害化処理を同時に行うことができ、しかも廃
液の発生の全くない脱硫システムが可能となるので、そ
の効果は極めて顕著であるということができる。
As explained above with the embodiments, according to the present invention,
It is said that the effect is extremely significant, as it enables a desulfurization system that simultaneously detoxifies fly ash from coal-fired power plants and sulfuric acid, a byproduct of flue gas desulfurization equipment, and does not generate any waste liquid. be able to.

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

第1図は本発明の一実施例を示す系統図、第2図は本発
明の他の実施例を示す系統図である。 1・・・・・・ボイラ、2・・・・・・集じん器、3・
・・・・・硫酸濃縮装置、4・・・・・・排煙脱硫装置
、5・・・・・・煙突、6・・・・・・濃縮硫酸タンク
、7・・・・・・硫酸供給ポンプ、8・・・・・・フラ
イアッシュホッパ、8″・・・・・・添加剤ホッパ、9
,9″・・・・定量フィーダ、10・・・・・・移送フ
ィーダ、11・・・・・中和反応器。
FIG. 1 is a system diagram showing one embodiment of the present invention, and FIG. 2 is a system diagram showing another embodiment of the invention. 1... Boiler, 2... Dust collector, 3.
... Sulfuric acid concentrator, 4 ... Flue gas desulfurization device, 5 ... Chimney, 6 ... Concentrated sulfuric acid tank, 7 ... Sulfuric acid supply Pump, 8...Fly ash hopper, 8''...Additive hopper, 9
, 9''...quantitative feeder, 10...transfer feeder, 11...neutralization reactor.

Claims (1)

【特許請求の範囲】 1 廃硫酸を石炭燃焼フライアッシュと混合して中和反
応により処理するに際し、中和反応前の混合物中に含ま
れる水の量を中和反応後の生成物が実質的に固化される
如く調整することを特徴とする廃硫酸の中和固化処理法
。 2 該反応前の混合物中に含まれる水の量を中和反応時
の蒸発水、反応生成物の結晶水、反応生成物固体表面の
水分の合計量であるように調整する特許請求の範囲第1
項記載の廃硫酸の中和固化処理法。 3 該廃硫酸の濃度を、該反応前の混合物中に含まれる
水の量が中和反応後の生成物が実質的に固化物となる如
く調整する特許請求の範囲第1項または第2項記載の廃
硫酸の中和固化処理法。 4 該中和反応前の混合物は、更に石灰、石灰石の如き
アルカリ性添加剤が添加されたものである特許請求の範
囲第1項乃至第3項の何れかに記載された廃硫酸の中和
固化処理法。 5 該中和反応による処理は、攪拌翼を備えた中和反応
器内において行うものである特許請求の範囲第1項乃至
第4項の何れかに記載された廃硫酸の中和固化処理法。
[Claims] 1. When waste sulfuric acid is mixed with coal combustion fly ash and treated by a neutralization reaction, the amount of water contained in the mixture before the neutralization reaction is reduced so that the product after the neutralization reaction is substantially reduced. A method for neutralizing and solidifying waste sulfuric acid, which is characterized by adjusting the waste sulfuric acid so that it is solidified. 2 The amount of water contained in the mixture before the reaction is adjusted to be the total amount of evaporated water during the neutralization reaction, crystallized water of the reaction product, and water on the solid surface of the reaction product. 1
Neutralization and solidification treatment method for waste sulfuric acid described in Section 1. 3. The concentration of the waste sulfuric acid is adjusted such that the amount of water contained in the mixture before the reaction substantially becomes a solidified product after the neutralization reaction. The method for neutralizing and solidifying waste sulfuric acid described above. 4. Neutralization and solidification of waste sulfuric acid according to any one of claims 1 to 3, wherein the mixture before the neutralization reaction is further added with an alkaline additive such as lime or limestone. Processing method. 5. A method for neutralizing and solidifying waste sulfuric acid according to any one of claims 1 to 4, wherein the neutralization reaction is carried out in a neutralization reactor equipped with a stirring blade. .
JP2387577A 1977-03-07 1977-03-07 Neutralization and solidification treatment method for waste sulfuric acid Expired JPS6043198B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2387577A JPS6043198B2 (en) 1977-03-07 1977-03-07 Neutralization and solidification treatment method for waste sulfuric acid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2387577A JPS6043198B2 (en) 1977-03-07 1977-03-07 Neutralization and solidification treatment method for waste sulfuric acid

Publications (2)

Publication Number Publication Date
JPS53108877A JPS53108877A (en) 1978-09-22
JPS6043198B2 true JPS6043198B2 (en) 1985-09-26

Family

ID=12122612

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2387577A Expired JPS6043198B2 (en) 1977-03-07 1977-03-07 Neutralization and solidification treatment method for waste sulfuric acid

Country Status (1)

Country Link
JP (1) JPS6043198B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08226626A (en) * 1995-02-20 1996-09-03 Nisshin Kiko Kk Dry ash treating system
KR20030071442A (en) * 2002-02-28 2003-09-03 박상숙 Solidification of coal fly ash by mixing sulfuric acid
FI120162B (en) 2005-02-17 2009-07-15 Foster Wheeler Energia Oy Vertebrate boiler plant and method for combustion of sulfur-containing fuel in a vertebrate boiler plant

Also Published As

Publication number Publication date
JPS53108877A (en) 1978-09-22

Similar Documents

Publication Publication Date Title
US5100633A (en) Method for scrubbing pollutants from an exhaust gas stream
CN103566726B (en) Calcined dolomite in powder denitrating flue gas desulfurization preparing magnesium hydroxide, magnesia and gypsum method
CN102126837B (en) Method for treating fly ash by water washing
GB2210035A (en) Scrubbing exhaust gas streams
WO2020204026A1 (en) Device and method pertaining to gas purification treatment and/or combustion ash neutralization treatment
US3855391A (en) Sludge stabilization with gypsum
JP2803855B2 (en) Sewage sludge recycling system
TWI795750B (en) Apparatus and method for combustion exhaust gas purification
US4540555A (en) Method of removing sulfur dioxide and other toxic and noxious components from flue gases
JP2013086981A (en) System and method for producing phosphatic fertilizer
JPS6043198B2 (en) Neutralization and solidification treatment method for waste sulfuric acid
US5324501A (en) Method for the preparation of low-chloride plaster products from calcium-containing residues of flue-gas purification plants
CN114452790B (en) Method for absorbing and mineralizing and utilizing carbon dioxide in waste gas
JP2886180B2 (en) Wastewater treatment method for wet desulfurization equipment
WO2001032324A1 (en) Method for treating combustion ash of coal and method for desulfurization
KR20100131895A (en) Method for absorbing co2 in the emission gas and recycling calcium carbonate by utilizing eluate of coal ash in the anthracite-fired fluidized-bed power plant
JP4387040B2 (en) Soil improver and / or organic fertilizer and method for producing the same
JP2758147B2 (en) Fly ash treatment method
CN102580498B (en) Comprehensive treatment method for high-concentration ammonia nitrogen waste water and boiler flue gas
JP5147146B2 (en) Waste incineration fly ash treatment method
JP2006035088A (en) Method for treating sludge and system for treating sludge
CA1302049C (en) Method and system for simultaneously scrubbing cement kiln exhaustgas and producing useful by-products therefrom
JPH0650505A (en) Desulfurizing agent used both for fuel and manufacture thereof
JP2002239530A (en) Method for treating incineration ash and incineration ash washing liquid
JP2008272574A (en) Method of suppressing elution of hexavalent chromium and thermal power generation system