JPH0571284B2 - - Google Patents

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Publication number
JPH0571284B2
JPH0571284B2 JP61096926A JP9692686A JPH0571284B2 JP H0571284 B2 JPH0571284 B2 JP H0571284B2 JP 61096926 A JP61096926 A JP 61096926A JP 9692686 A JP9692686 A JP 9692686A JP H0571284 B2 JPH0571284 B2 JP H0571284B2
Authority
JP
Japan
Prior art keywords
calcium
curing
water
flue gas
mixed
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 - Fee Related
Application number
JP61096926A
Other languages
Japanese (ja)
Other versions
JPS62254824A (en
Inventor
Tsutomu Ueno
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.)
Hokkaido Electric Power Co Inc
Original Assignee
Hokkaido Electric Power Co Inc
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 Hokkaido Electric Power Co Inc filed Critical Hokkaido Electric Power Co Inc
Priority to JP61096926A priority Critical patent/JPS62254824A/en
Priority to SE8700411A priority patent/SE465606B/en
Priority to NL8700352A priority patent/NL190924C/en
Priority to IT19427/87A priority patent/IT1202568B/en
Priority to AT0103187A priority patent/AT395683B/en
Priority to DK216687A priority patent/DK216687A/en
Publication of JPS62254824A publication Critical patent/JPS62254824A/en
Publication of JPH0571284B2 publication Critical patent/JPH0571284B2/ja
Granted legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/041Oxides or hydroxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/045Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium containing sulfur, e.g. sulfates, thiosulfates, gypsum
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/046Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium containing halogens, e.g. halides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/103Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/3028Granulating, agglomerating or aggregating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/42Materials comprising a mixture of inorganic materials

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  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Compositions Of Oxide Ceramics (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

〔産業上の利用分野〕 本発明は排煙処理剤さらに詳しくは石炭、重油
等の燃料および各種廃棄物の燃焼に伴う排ガスの
処理剤の製造方法に関する。 〔従来の技術〕 石炭、重油等の燃料および各種廃棄物の燃焼に
伴い発生する排ガス中に含まれる硫黄酸化物およ
び窒化酸化物、塩化物、弗化物等は、建物、構築
物等に害を与えるばかりでなく、動植物さらには
人体にも極めて大きな影響を及ぼすことが判明
し、排ガス中の上記物質を除去する方法が研究さ
れ、多種多様な方法が開発されている。 これらの方法のうち特に硫黄酸化物および窒素
酸化物を除去するいわゆる脱硫・脱硝法は乾式法
および湿式法に大別される。本発明の属する乾式
法には第1表に示す方法が知られている。
[Industrial Field of Application] The present invention relates to a flue gas treatment agent, and more particularly to a method for producing a flue gas treatment agent for flue gas generated from combustion of fuels such as coal and heavy oil and various wastes. [Prior art] Sulfur oxides, nitride oxides, chlorides, fluorides, etc. contained in the exhaust gas generated from the combustion of fuels such as coal and heavy oil and various wastes are harmful to buildings, structures, etc. In addition, it has been found that they have an extremely large effect on animals, plants, and even the human body, and methods for removing the above-mentioned substances from exhaust gas have been researched and a wide variety of methods have been developed. Among these methods, the so-called desulfurization and denitrification methods, which specifically remove sulfur oxides and nitrogen oxides, are broadly classified into dry methods and wet methods. Among the dry methods to which the present invention pertains, the methods shown in Table 1 are known.

【表】【table】

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

本発明の目的は、上述の従来の乾式脱硫および
脱硝方法の種々の問題点を解決し、脱硫と脱硝を
同時に行い、さらに塩化物、弗化物等も除去する
ことも可能な成形容易な排煙処理剤の製造方法を
提供することにある。 〔問題点を解決するための手段〕 本発明は、酸化カルシウムおよび/または水酸
化カルシウムを含有する物質と、硫酸化合物、ハ
ロゲン元素化合物、二酸化ケイ素を含有する物
質、酸化アルミニウムを含有する物質、硫化物、
およびアルカリ金属の水酸化物からなる群から選
ばれた1種以上の物質とを水と混合し、湿空養生
又は蒸気養生した後成形し、再度湿空養生又は蒸
気養生を行い、そのまま又は30℃以上の温度で熱
処理することを特徴とする排煙処理剤の製造方法
である。 本発明の酸化カルシウムおよび/または水酸化
カルシウムを含有する物質としては、例えば生石
灰、消石灰、セメント、スラグ、ドロマイトプラ
スター(石灰含有)およびアセチレン滓等の副生
品等があげられる。 硫酸化合物、ハロゲン元素化合物とは、例えば
カルシウム、マグネシウム等のアルカリ土類金
属、ナトリウム、カリウム等のアルカリ金属と硫
酸、ハロゲン化水素とを組合わせることによつて
生成する物質で硫酸カルシウム、硫酸マグネシウ
ム、塩化カルシウム、塩化マグネシウム、硫酸ナ
トリウム、硫酸カリウム、亜硫酸カルシウム、硫
酸水素カルシウム、塩化ナトリウム、塩化ストロ
ンチウム、臭化カルシウム、ヨウ化カルシウム、
塩化カリウム、チオ硫酸ナトリウム、黒液燃焼灰
等があげられる。 二酸化ケイ素を含有する物質としては、例えば
ケイ酸、含水ケイ酸、メタケイ酸、ケイ酸アルミ
ニウム、ケイ酸カルシウムおよびクリストバライ
ト、トリジマイト、カオリン、ベントナイト、タ
ルク、パーライト、シラス、ケイソウ土、ガラス
等反応性二酸化ケイ素を含有する化合物があげら
れる。 酸化アルミニウムを含有する物質としては、例
えばアルミナ、ケイ酸アルミニウム、ベントナイ
ト、カオリン、ケイソウ土、ゼオライト、パーラ
イト、ボーキサイト等反応性酸化アルミニウムを
含有する化合物等があげられる。 硫化物としては、例えば硫化カルシウム、硫化
鉄、硫化亜鉛があげられる。 アルカリ金属の水酸化物としては、水酸化ナリ
トウム、水酸化カリウム等があげられる。 さらにこれまでに記述した所要材料が、例えば
単体イオウを添加することによつて材料間の相互
の反応が進行し、その結果硫化カルシウム、硫酸
カルシウム等を生成して供給されるような場合、
さらに、ケイ酸と苛性アルカリが反応して生成さ
れる水ガラス等も含まれる。 また前述の8種の物質中2種以上を同時に含有
する他の物質の例として、石炭灰および石炭流動
層燃焼灰(酸化カルシウム、二酸化ケイ素、酸化
アルミニウム、硫酸カルシウム、硫酸ナトリウ
ム、硫酸カリウム源)、セメントおよびセメント
クリンカー(酸化カルシウム、硫酸カルシウム、
二酸化ケイ素、酸化アルミニウム源)、スラグお
よびシラス、安山岩、チヤート、石英粗面岩、オ
パール、沸石、長石、粘土鉱物、エトリンガイド
(酸化ナトリウム、二酸化ケイ素、酸化アルミニ
ウム、酸化カルシウム)等の反応性二酸化ケイ
素、ナトリウム、アルミニウム、カルシウム等お
よび塩化物、硫酸塩等を含有する鉱物、さらに流
動層燃焼灰等の炉内脱硫灰および煙道脱硫後の廃
脱硫剤等があげられる。 本発明者らは、上記8種の物質(酸化カルシウ
ム、水酸化カルシウム、硫酸化合物、ハロゲン元
素化合物、二酸化ケイ素、酸化アルミニウム、硫
化物、アルカリ金属の水酸化物)(以下これらを
基材と略記する)を種々組合わせ、水と混合し硬
化させ、排煙処理の試験を行い、その組合わせと
調製方法によつては、予期しない性能を示すこと
を見出し本発明を完成した。 前記酸化カルシウムおよび/または水酸化カル
シウムを含有する物質にアルカリ土類金属、アル
カリ金属の硫酸化合物、あるいはハロゲン元素化
合物、二酸化ケイ素を含有する物質、酸化アルミ
ニウムを含有する物質、硫化物、アルカリ金属の
水酸化物を次のような配合による組合わせによつ
て著しく優れた排煙処理性能が得られる。 基材の配合割合は CaOとして少なくとも 1% アルカリ土類金属あるいはアルカリ金属の硫酸
化合物および/またはハロゲン元素化合物とし
て少なくとも 0.1% SiO2として 0〜90% Al2O3として 0〜70% 硫化物として少なくとも 0.1% アルカリ金属の水酸化物として少なくとも 0.1% 好ましくは CaOとして 1〜80% アルカリ土類金属あるいはアルカリ金属の硫酸
化合物および/またはハロゲン元素化合物とし
て好ましくはCaSO4,Na2SO4,CaCl2,NaCl
の1種または2種以上が 0.1〜70% SiO2として 5〜90% Al2O3として 5〜70% 硫化物として好ましくは硫化カルシウムが 0.1〜50% アルカリ金属の水酸化物として好ましくは
NaOHおよび/またはKOHが 0.1〜10% である。 原料を必要により粉砕後混合し、さらに水を加
えて混合する。水溶性塩類は事前に水に溶解して
使用する。添加する水の量は乾物100部当たり、
好ましくは約20部〜約80部、より好ましくは約37
部〜約70部である。 ついで得られたスラリー状又は泥状の混合物を
第1段階の湿空養生または蒸気養生を行う。この
時の湿空養生の条件は、温度10℃〜40℃、相対湿
度50%〜100%で数分間から数十時間が好ましい。
また蒸気養生は、温度40℃〜180℃、相対湿度100
%で数分間から48時間が好ましい。この養生工程
は、本発明の排煙処理材の排煙処理反応を進行さ
せるための処理剤中の活性物質の生成に必要な水
分を充分に与えた状態を経て、成形するためには
不可欠である。スラリー状又は泥状の混合物は、
この工程を経ることによつて、排煙処理に必要な
活性化合物形成の重要な初期段階を終了し、この
間水分の大部分は該化合物形成反応に消費される
のであつて、第1段階の養生は、養生終了後に混
合物の成形・造粒するために適当な水分状態にな
るような条件で行うことが好ましい。 次に第1段階の養生を経た物質をブリケツトマ
シーン等によつて成形あるいはペレタイザー等に
よつて成形(造粒)する。成形は、上述の工程を
経るため容易にかつ歩留まりよく行われる。 この成形物を第2段階の養生を行い、整粒して
本発明の排煙処理剤を得ることができる。 第2段階の養生は、湿空養生では10℃〜40℃、
相対湿度50%〜100%では1日〜1週間程度が好
ましく、また蒸気養生では温度40℃〜180℃、相
対湿度100%で10分間から72時間が好ましい。 さらに養生後の成形物を30℃以上、好ましくは
50℃〜200℃の範囲で0.3〜10時間熱処理すること
によつて、より処理剤の性能を向上させることが
できる。 以下実施例をあげてさらに詳細に説明する。 実施例 1 市販の消石灰に第2表にその化学組成を示す石
炭灰を混合し、塩化カルシウムに水を加えて溶解
した液を第4表に示す配合に従つて混合し水を加
えて再度混合する。次に常圧100℃の蒸気養生を
1時間行い、得られた柔らかい硬化物を5mm目の
フルイに通し造粒のための種子を造りチユーブ型
ペレタイザーによつて造粒し、再度100℃常圧蒸
気養生を6時間行う。得られた造粒物を1.7mm〜
2.5mmに整粒し、そのまま(未乾燥品、実施例1
−1)および130℃、2時間熱処理して(実施例
1−2)本発明の排煙処理剤を得た。 性能試験は、第3表に示す条件(空間速度
6000h-1)でガス温度130℃における脱硫脱硝試験
(SO2,NOx除去試験)を行つた。なお比表面積
も測定した。比表面積の測定は、試料を200℃で
脱ガスした後BET法で行つた。これらの結果を
第5表に示した。
The purpose of the present invention is to solve the various problems of the conventional dry desulfurization and denitrification methods described above, and to provide an easily molded flue gas that can simultaneously perform desulfurization and denitrification and also remove chlorides, fluorides, etc. An object of the present invention is to provide a method for producing a processing agent. [Means for Solving the Problems] The present invention provides a substance containing calcium oxide and/or calcium hydroxide, a sulfuric acid compound, a halogen element compound, a substance containing silicon dioxide, a substance containing aluminum oxide, and a substance containing calcium oxide and/or calcium hydroxide. thing,
and one or more substances selected from the group consisting of alkali metal hydroxides, mixed with water, subjected to humid air curing or steam curing, molded, and then humid air curing or steam curing again. This is a method for producing a flue gas treatment agent, which is characterized by heat treatment at a temperature of 0.degree. C. or higher. Examples of substances containing calcium oxide and/or calcium hydroxide of the present invention include by-products such as quicklime, slaked lime, cement, slag, dolomite plaster (containing lime), and acetylene slag. Sulfuric compounds and halogen element compounds are substances produced by combining alkaline earth metals such as calcium and magnesium, alkali metals such as sodium and potassium, and sulfuric acid and hydrogen halides, such as calcium sulfate and magnesium sulfate. , calcium chloride, magnesium chloride, sodium sulfate, potassium sulfate, calcium sulfite, calcium hydrogen sulfate, sodium chloride, strontium chloride, calcium bromide, calcium iodide,
Examples include potassium chloride, sodium thiosulfate, and black liquor combustion ash. Substances containing silicon dioxide include, for example, silicic acid, hydrous silicic acid, metasilicic acid, aluminum silicate, calcium silicate, cristobalite, tridymite, kaolin, bentonite, talc, perlite, shirasu, diatomaceous earth, glass, etc. Examples include compounds containing silicon. Examples of substances containing aluminum oxide include compounds containing reactive aluminum oxide, such as alumina, aluminum silicate, bentonite, kaolin, diatomaceous earth, zeolite, perlite, and bauxite. Examples of sulfides include calcium sulfide, iron sulfide, and zinc sulfide. Examples of the alkali metal hydroxide include sodium hydroxide and potassium hydroxide. Furthermore, when the required materials described so far are supplied by adding elemental sulfur, for example, the mutual reaction between the materials proceeds, resulting in the production of calcium sulfide, calcium sulfate, etc.
Furthermore, it also includes water glass produced by the reaction of silicic acid and caustic alkali. Examples of other substances that simultaneously contain two or more of the eight substances mentioned above include coal ash and coal fluidized bed combustion ash (sources of calcium oxide, silicon dioxide, aluminum oxide, calcium sulfate, sodium sulfate, potassium sulfate). , cement and cement clinker (calcium oxide, calcium sulfate,
silicon dioxide, aluminum oxide sources), slag and shirasu, andesite, chaat, quartz trachyte, opal, zeolite, feldspar, clay minerals, ettrin guides (sodium oxide, silicon dioxide, aluminum oxide, calcium oxide), etc. Examples include minerals containing silicon dioxide, sodium, aluminum, calcium, etc., chlorides, sulfates, etc., as well as in-furnace desulfurization ash such as fluidized bed combustion ash, and waste desulfurization agents after flue desulfurization. The present inventors have discovered the above eight types of substances (calcium oxide, calcium hydroxide, sulfuric acid compounds, halogen element compounds, silicon dioxide, aluminum oxide, sulfides, alkali metal hydroxides) (hereinafter these are abbreviated as base materials). The present invention was completed based on the discovery that various combinations of the following materials were combined, mixed with water and cured, and tested for flue gas treatment, and that depending on the combination and preparation method, unexpected performance was exhibited. The substance containing calcium oxide and/or calcium hydroxide may be an alkaline earth metal, a sulfuric acid compound of an alkali metal, or a halogen element compound, a substance containing silicon dioxide, a substance containing aluminum oxide, a sulfide, or a sulfuric acid compound of an alkali metal. Extremely excellent flue gas treatment performance can be obtained by combining hydroxides in the following formulation. The proportion of the base material is at least 1% as CaO, at least 0.1% as a sulfuric acid compound of an alkaline earth metal or alkali metal and/or a halogen element compound, as SiO 2 0-90% as Al 2 O 3 0-70% as sulfide. At least 0.1% At least 0.1% as alkali metal hydroxide, preferably as CaO 1 to 80% As alkaline earth metal or alkali metal sulfuric acid compounds and/or halogen element compounds, preferably CaSO 4 , Na 2 SO 4 , CaCl 2 , NaCl
0.1-70% as SiO 2 5-90% as Al 2 O 3 5-70% as Al 2 O 3 Preferably calcium sulfide as sulfide 0.1-50% as alkali metal hydroxide
NaOH and/or KOH is 0.1-10%. The raw materials are mixed after being crushed if necessary, and water is further added and mixed. Water-soluble salts are dissolved in water before use. The amount of water added is per 100 parts of dry matter,
Preferably about 20 parts to about 80 parts, more preferably about 37 parts.
~70 copies. The resulting slurry or slurry mixture is then subjected to a first stage of wet air curing or steam curing. The conditions for moist air curing at this time are preferably a temperature of 10° C. to 40° C. and a relative humidity of 50% to 100% for several minutes to several tens of hours.
In addition, steam curing requires a temperature of 40°C to 180°C and a relative humidity of 100°C.
% for several minutes to 48 hours. This curing step is essential for molding the flue gas treatment material of the present invention after providing sufficient moisture necessary for the generation of active substances in the treatment agent to advance the flue gas treatment reaction. be. A slurry or muddy mixture is
By going through this step, the important initial stage of active compound formation necessary for flue gas treatment is completed, during which most of the water is consumed in the compound formation reaction, and the first stage of curing is completed. It is preferable to carry out this under conditions such that an appropriate moisture state is obtained for molding and granulating the mixture after curing. Next, the material that has undergone the first stage of curing is molded using a briquette machine or the like or molded (granulated) using a pelletizer or the like. Molding is performed easily and with a high yield because it goes through the steps described above. This molded product undergoes a second stage of curing and is sized to obtain the flue gas treatment agent of the present invention. The second stage of curing is 10℃ to 40℃ in moist air curing.
At a relative humidity of 50% to 100%, a period of about 1 day to 1 week is preferable, and for steam curing, a period of from 10 minutes to 72 hours at a temperature of 40° C. to 180° C. and a relative humidity of 100% is preferable. Furthermore, after curing, the molded product should be kept at a temperature above 30℃, preferably
The performance of the processing agent can be further improved by performing heat treatment in the range of 50°C to 200°C for 0.3 to 10 hours. The present invention will be described in more detail below with reference to Examples. Example 1 Commercially available slaked lime was mixed with coal ash, the chemical composition of which is shown in Table 2, and a solution of calcium chloride and water was mixed according to the formulation shown in Table 4, water was added, and the mixture was mixed again. do. Next, steam curing at 100°C under normal pressure was performed for 1 hour, and the obtained soft cured product was passed through a 5 mm sieve to prepare seeds for granulation, which was then granulated using a tube pelletizer, and again at 100°C under normal pressure. Steam curing is performed for 6 hours. The obtained granules are 1.7 mm ~
Sorted to 2.5 mm and as it is (undried product, Example 1)
-1) and 130°C for 2 hours to obtain a flue gas treatment agent of the present invention (Example 1-2). The performance test was conducted under the conditions shown in Table 3 (space velocity
A desulfurization and denitrification test (SO 2 , NO x removal test) was conducted at a gas temperature of 130°C (6000h -1 ). Note that the specific surface area was also measured. The specific surface area was measured by the BET method after degassing the sample at 200°C. These results are shown in Table 5.

【表】【table】

【表】 実施例 2 市販の消石灰に石炭灰を混合し、塩化カルシウ
ムに水を加えて溶解して液を第4表に示す割合で
混合し、水を加えて再度混合し、常圧100℃の蒸
気養生を1時間行い、得られた柔らかい硬化物を
5mm目のフルイに通し造粒のための種子を造り、
パン型ペレタイザーによつて造粒し、再度125℃
の高圧蒸気養生を3時間行い、得られた造粒物を
1.7〜2.5mmに整粒し、130℃、2時間熱処理して
本発明の排煙処理剤を得た。 性能試験は、実施例1と同様の条件で行い、得
られた結果を第5表に示した。 実施例 3 市販の消石灰に石炭灰、硫酸カルシウムを第4
表に示す配合に従つて混合し、水を加えて混合す
る。 以下、実施例1と同様にして未熱処理(実施例
3−1)と熱処理(実施例3−2)の本発明方法
による排煙脱硫剤を得て、実施例1と同様の条件
で試験を行い、第5表のような結果が得られた。 実施例 4 市販の消石灰に石炭灰、硫酸カルシウムを第4
表に示す割合で加えて混合し、水を加えて水分を
原料乾物100重量部当たり42部とし再度混合する。
次に常圧100℃の蒸気養生を1時間行い、得られ
た柔らかい硬化物を5mm目のフルイに通し造粒の
ための種子を造りパン型ペレタイザーによつて造
粒し、再度100℃常圧蒸気養生を6時間行う。得
られた造粒物を破砕して0.5〜0.71mmに整粒し、
130℃、2時間熱処理して本発明の排煙処理剤を
得た。 性能試験は、空間速度10000h-1とした以外は実
施例1と同じ条件で行い、その結果を第5表に示
した。 実施例 5〜14 市販の消石灰および石炭灰に第4表に示すよう
にそれぞれ[MgSO4],[CaCl2+S],[CaCl2
FeS],[NaCl],[KCl],[Na2SO4],[K2SO4],
[S2Cl2],[MgCl2],[CaSO4+Na2S2O3]を混合
する、この場合、消石灰、石炭灰を除く原料が水
に溶解性の場合は使用水量の一部で溶解し、消石
灰、石炭灰を粉体混合した後に、その水溶液を加
え、残りの使用水を加えて混合した。 以下、実施例4と同様にして、造粒物を得、性
能試験を行い第5表のような結果が得られた。 実施例 15〜16 市販の消石灰、ケイ酸、水酸化アルミニウムを
第4表に示す割合で混合し、塩化カルシウム水溶
液を加えて再度混合する。 以下、実施例4と同様にして造粒物を得、性能
試験を行い第5表のような結果が得られた。 実施例 17 市販の消石灰、ケイ酸を混合し、塩化カルシウ
ム水溶液を加えて第4表に示す割合とし再度混合
する。 以下、実施例4と同様にして造粒物を得、性能
試験を行い第5表のような結果が得られた。 実施例 18 市販の消石灰、ケイ酸を第4表に示す割合で混
合し、水を加えて再度混合する。 以下、実施例4と同様にして造粒物を得、性能
試験を行い第5表のような結果が得られた。 実施例 19 市販の消石灰、石炭灰にイオウを第4表に示す
割合として混合し、水を加えて再度混合する。 以下、実施例4と同様にして造粒物を得、性能
試験を行い第5表のような結果が得られた。 実施例 20 市販の消石灰に石炭灰を加え混合後、水酸化ナ
トリウムに水を加えて溶解した液を第4表に示す
配合に従つて混合し、水を加えて再度混合する。 以下、実施例4と同様にして造粒物を得、性能
試験を行い第5表のような結果が得られた。 比較例 1 パン型ペレタイザーで造粒した後の100℃、6
時間常圧蒸気養生を省略した以外は、実施例4と
同様にして剤を得、実施例4と同様の性能試験を
行い、第5表のような結果を得た。 比較例 2 市販の消石灰に石炭灰を混合し、塩化カルシウ
ムに水を加えて溶解した液を第4表に示す配合に
従つて混合し、水を加えて再度混合する。次に第
1段階の養生を行うことなく実施例1と同様の造
粒工程に移つたが、水量42%では混合物が非常に
柔らかく機械的に造粒、成形することは、全く不
可能であつた。このため性能試験用剤を一個一個
手で丸めて製造した。次に100℃、6時間常圧蒸
気養生を行い、0.5〜0.71mmに整粒し、130℃、2
時間熱処理して比較試料を得、実施例1と同様の
性能試験を行い、その結果を第5表に示した。 比較例 3 市販の消石灰に石炭灰を混合し、硫酸カルシウ
ムを第4表に示す配合に従つて混合し、水を加え
て再度混合する。次に第1段階の養生を行うこと
なく実施例1と同様の造粒工程に移つたが、水量
42%では混合物が非常に柔らかく機械的に造粒、
成形することは、全く不可能であつた。このため
性能試験用剤を一個一個手で丸めて製造した。次
に100℃、6時間常圧蒸気養生を行い、0.5〜0.71
mmに整粒し、130℃、2時間熱処理して比較試料
を得、実施例1と同様の性能試験を行い、その結
果を第5表に示した。
[Table] Example 2 Coal ash was mixed with commercially available slaked lime, water was added to calcium chloride to dissolve it, the liquid was mixed at the ratio shown in Table 4, water was added and mixed again, and the mixture was heated at normal pressure at 100°C. After steam curing for 1 hour, the resulting soft cured product was passed through a 5 mm sieve to produce seeds for granulation.
Pelletize using a pan-type pelletizer and heat to 125℃ again.
High-pressure steam curing was performed for 3 hours, and the resulting granules were
The particles were sized to 1.7 to 2.5 mm and heat treated at 130°C for 2 hours to obtain the flue gas treatment agent of the present invention. The performance test was conducted under the same conditions as in Example 1, and the results are shown in Table 5. Example 3 Adding coal ash and calcium sulfate to commercially available slaked lime
Mix according to the formulation shown in the table, add water and mix. Hereinafter, in the same manner as in Example 1, flue gas desulfurization agents were obtained by the method of the present invention, unheated (Example 3-1) and heat treated (Example 3-2), and tested under the same conditions as in Example 1. The results shown in Table 5 were obtained. Example 4 Coal ash and calcium sulfate were added to commercially available slaked lime.
Add and mix in the proportions shown in the table, then add water to make the moisture content 42 parts per 100 parts by weight of raw material dry matter and mix again.
Next, steam curing at 100°C under normal pressure was performed for 1 hour, and the resulting soft cured product was passed through a 5 mm sieve to prepare seeds for granulation, granulated using a pan-type pelletizer, and again at 100°C under normal pressure. Steam curing is performed for 6 hours. The obtained granules are crushed and sized to 0.5 to 0.71 mm,
A heat treatment was performed at 130°C for 2 hours to obtain a flue gas treatment agent of the present invention. The performance test was conducted under the same conditions as in Example 1 except that the space velocity was 10,000 h -1 , and the results are shown in Table 5. Examples 5 to 14 Commercially available slaked lime and coal ash were contaminated with [MgSO 4 ], [CaCl 2 +S], and [CaCl 2 + ], respectively, as shown in Table 4.
FeS], [NaCl], [KCl], [Na 2 SO 4 ], [K 2 SO 4 ],
[S 2 Cl 2 ], [MgCl 2 ], [CaSO 4 + Na 2 S 2 O 3 ]. In this case, if the raw materials other than slaked lime and coal ash are soluble in water, a portion of the amount of water used is After dissolving, slaked lime, and coal ash were mixed in powder, an aqueous solution thereof was added, and the remaining water used was added and mixed. Thereafter, granules were obtained in the same manner as in Example 4, and performance tests were conducted, with the results shown in Table 5 being obtained. Examples 15-16 Commercially available slaked lime, silicic acid, and aluminum hydroxide are mixed in the proportions shown in Table 4, and an aqueous calcium chloride solution is added and mixed again. Thereafter, a granulated product was obtained in the same manner as in Example 4, and a performance test was conducted, and the results shown in Table 5 were obtained. Example 17 Commercially available slaked lime and silicic acid are mixed, an aqueous calcium chloride solution is added, and the mixture is mixed again at the proportions shown in Table 4. Thereafter, a granulated product was obtained in the same manner as in Example 4, and a performance test was conducted, and the results shown in Table 5 were obtained. Example 18 Commercially available slaked lime and silicic acid are mixed in the proportions shown in Table 4, water is added, and the mixture is mixed again. Thereafter, a granulated product was obtained in the same manner as in Example 4, and a performance test was conducted, and the results shown in Table 5 were obtained. Example 19 Commercially available slaked lime and coal ash are mixed with sulfur in the proportions shown in Table 4, water is added, and the mixture is mixed again. Thereafter, a granulated product was obtained in the same manner as in Example 4, and a performance test was conducted, and the results shown in Table 5 were obtained. Example 20 Coal ash is added to commercially available slaked lime and mixed. A solution obtained by adding water to sodium hydroxide is mixed according to the formulation shown in Table 4, and water is added and mixed again. Thereafter, a granulated product was obtained in the same manner as in Example 4, and a performance test was conducted, and the results shown in Table 5 were obtained. Comparative example 1 100℃ after granulation with a pan-type pelletizer, 6
A preparation was prepared in the same manner as in Example 4, except that the atmospheric pressure steam curing was omitted, and the same performance tests as in Example 4 were conducted, and the results shown in Table 5 were obtained. Comparative Example 2 Coal ash is mixed with commercially available slaked lime, and a solution obtained by adding water to calcium chloride is mixed according to the formulation shown in Table 4, and water is added and mixed again. Next, we proceeded to the same granulation process as in Example 1 without performing the first stage of curing, but with a water content of 42%, the mixture was so soft that it was completely impossible to mechanically granulate and mold it. Ta. For this purpose, the performance test preparations were manufactured by rolling them one by one by hand. Next, steam curing at 100℃ for 6 hours at normal pressure, grading to 0.5 to 0.71mm, and heating at 130℃ for 2 hours.
A comparative sample was obtained by heat treatment for a period of time, and the same performance test as in Example 1 was conducted, and the results are shown in Table 5. Comparative Example 3 Coal ash is mixed with commercially available slaked lime, calcium sulfate is mixed according to the formulation shown in Table 4, and water is added and mixed again. Next, the same granulation process as in Example 1 was carried out without performing the first stage of curing, but the amount of water
At 42% the mixture is very soft and mechanically granulated;
It was completely impossible to mold it. For this purpose, the performance test preparations were manufactured by rolling them one by one by hand. Next, normal pressure steam curing was performed at 100℃ for 6 hours, and the temperature was 0.5~0.71.
Comparative samples were obtained by sizing them to a size of 1.5 mm and heat-treated at 130° C. for 2 hours, and the same performance tests as in Example 1 were conducted, and the results are shown in Table 5.

【表】【table】

【表】【table】

【表】【table】

【表】【table】

【表】 * 試験用ガス通気後3時間の積分
除去率
実施例 21〜23 実施例1−2で得た排煙処理剤を破砕して0.5
〜0.71mmに整粒し、第3表中に示し模模ガスに実
施例21においてはHCl 200ppmを、実施例22では
HF 100ppmを、実施例23ではSO3500ppmになる
ようにそれぞれ加え、同表の試験条件(空間速度
は10000h-1)で除去試験を行つた。得られた結果
は次表のようである。
[Table] * Integral for 3 hours after test gas ventilation Removal rate Examples 21 to 23 The flue gas treatment agent obtained in Example 1-2 was crushed to 0.5
The grains were sized to ~0.71 mm, and 200 ppm of HCl was added to the simulated gas in Example 21 and in Example 22 as shown in Table 3.
100 ppm of HF and 500 ppm of SO 3 were added in Example 23, respectively, and a removal test was conducted under the test conditions shown in the same table (space velocity: 10000 h -1 ). The results obtained are shown in the table below.

〔発明の効果〕〔Effect of the invention〕

本発明方法になる排煙処理剤は、これまでの吸
収、吸着剤と異なり、その原料は酸化カルシウム
および/または水酸化カルシウムを含有する物質
と、硫酸化合物、ハロゲン元素化合物、二酸化ケ
イ素を含有する物質、酸化アルミニウムを含有す
る物質、硫化物およびアルカリ金属の水酸化物か
らなる群から選ばれた1種以上の物質とであるた
め、石炭灰、セメント、スラグ、ガラス屑、流動
層燃焼灰、炉内脱硫灰等も使用することができ、
使用可能原料は低廉で広範である。さらに製造工
程は比較的簡単であり、製造装置も特に精巧なも
のを必要としなので、生産費は従来品に比べて有
利である。また本発明の特徴である第1段階の養
生→成型→第2段階の養生の工程を経ることによ
つて、処理剤中の活性物質の生成に必要な水分を
充分に与えた状態で造粒、成形が可能となり、か
つ養生が充分行われ、安定した排煙処理性能をも
つ排煙処理剤が得られる。 本発明の方法による排煙処理剤は脱硫・脱硝の
性能は高く、かつHCl,HF等の除去についても
優れた能力を示すので、燃料の燃焼排ガスのみな
らず各種廃棄物の燃焼により排ガスの処理も効果
的に行うことができ、公害防止に大きく寄与する
ことができる。 また前述のように、本発明方法において原料と
して石炭灰、スラグ、ガスラ屑、流動層燃焼灰、
炉内脱硫灰等の廃棄物を活用することができるた
め、資源化技術としても有用である。
The flue gas treatment agent produced by the method of the present invention differs from conventional absorption and adsorption agents in that its raw materials contain a substance containing calcium oxide and/or calcium hydroxide, a sulfuric acid compound, a halogen element compound, and silicon dioxide. Coal ash, cement, slag, glass waste, fluidized bed combustion ash, In-furnace desulfurization ash, etc. can also be used,
Available raw materials are inexpensive and wide-ranging. Furthermore, the manufacturing process is relatively simple and the manufacturing equipment does not require particularly sophisticated equipment, so the production cost is advantageous compared to conventional products. In addition, by going through the steps of curing in the first stage → molding → curing in the second stage, which is a feature of the present invention, granulation can be carried out in a state where sufficient moisture is provided to generate the active substance in the treatment agent. It is possible to obtain a flue gas treatment agent that can be molded, is sufficiently cured, and has stable flue gas treatment performance. The flue gas treatment agent produced by the method of the present invention has high desulfurization and denitrification performance, and also shows excellent ability to remove HCl, HF, etc., so it can treat flue gas not only by burning fuel combustion flue gas but also by burning various wastes. can also be carried out effectively and can greatly contribute to pollution prevention. Further, as mentioned above, the raw materials used in the method of the present invention include coal ash, slag, gas slag, fluidized bed combustion ash,
Since waste such as in-furnace desulfurization ash can be utilized, it is also useful as a resource recycling technology.

Claims (1)

【特許請求の範囲】[Claims] 1 酸化カルシウムおよび/または水酸化カルシ
ウムを含有する物質と、硫酸化合物、ハロゲン元
素化合物、二酸化ケイ素を含有する物質、酸化ア
ルミニウムを含有する物質、硫化物、およびアル
カリ金属の水酸化物からなる群から選ばれた1種
以上の物質とを水と混合し、湿空養生または蒸気
養生した後成形し、再度湿空養生または蒸気養生
を行い、そのまままたは30℃以上の温度で熱処理
することを特徴とする排煙処理剤の製造方法。
1. From the group consisting of substances containing calcium oxide and/or calcium hydroxide, sulfuric compounds, halogen element compounds, substances containing silicon dioxide, substances containing aluminum oxide, sulfides, and alkali metal hydroxides. It is characterized by mixing one or more selected substances with water, curing in humid air or steam, forming it, curing in humid air or steam again, and then heat-treating it as it is or at a temperature of 30°C or higher. A method for producing a flue gas treatment agent.
JP61096926A 1986-04-28 1986-04-28 Production of treating agent for flue gas Granted JPS62254824A (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
JP61096926A JPS62254824A (en) 1986-04-28 1986-04-28 Production of treating agent for flue gas
SE8700411A SE465606B (en) 1986-04-28 1987-02-04 PROCEDURES FOR PREPARING A SMOKE TREATMENT AGENT
NL8700352A NL190924C (en) 1986-04-28 1987-02-13 Process for the preparation of a treatment agent for combustion gases.
IT19427/87A IT1202568B (en) 1986-04-28 1987-02-19 PROCEDURE FOR THE PREPARATION OF AGENTS FOR THE TREATMENT OF GASEOUS COMBUSTION PRODUCTS
AT0103187A AT395683B (en) 1986-04-28 1987-04-24 Exhaust gas cleaning agent - useful for removing sulphur- and nitrogen-oxide(s) also hydrochloric- and hydrofluoric- acids
DK216687A DK216687A (en) 1986-04-28 1987-04-28 PROCEDURE FOR THE MANUFACTURING OF MEASURES FOR TREATMENT OF ROEGAS GAS

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61096926A JPS62254824A (en) 1986-04-28 1986-04-28 Production of treating agent for flue gas

Publications (2)

Publication Number Publication Date
JPS62254824A JPS62254824A (en) 1987-11-06
JPH0571284B2 true JPH0571284B2 (en) 1993-10-06

Family

ID=14177953

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61096926A Granted JPS62254824A (en) 1986-04-28 1986-04-28 Production of treating agent for flue gas

Country Status (6)

Country Link
JP (1) JPS62254824A (en)
AT (1) AT395683B (en)
DK (1) DK216687A (en)
IT (1) IT1202568B (en)
NL (1) NL190924C (en)
SE (1) SE465606B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03101812A (en) * 1987-12-09 1991-04-26 Yoshio Kobayashi Method for dry-purifying waste gas
GB9926898D0 (en) 1999-11-12 2000-01-12 School Of Earth & Environmenta Calcium silicate sorbents
TWI580658B (en) * 2016-08-04 2017-05-01 Gfc Bioenvirotek Co Ltd The usage of fly ash from flue gas desulfurization to make compositiong for building materials
CN106622273A (en) * 2016-12-26 2017-05-10 北京神雾环境能源科技集团股份有限公司 Denitration catalyst and preparation method thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62183839A (en) * 1986-02-06 1987-08-12 Kawasaki Heavy Ind Ltd Preparation of flue gas desulfurizing agent

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58166932A (en) * 1982-03-26 1983-10-03 Onoda Cement Co Ltd Removing agent for acidic material in waste gas
JPS59136133A (en) * 1983-01-25 1984-08-04 Babcock Hitachi Kk Manufacture of acidic gas absorbent

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62183839A (en) * 1986-02-06 1987-08-12 Kawasaki Heavy Ind Ltd Preparation of flue gas desulfurizing agent

Also Published As

Publication number Publication date
NL190924B (en) 1994-06-01
IT8719427A0 (en) 1987-02-19
SE8700411D0 (en) 1987-02-04
NL190924C (en) 1994-11-01
SE465606B (en) 1991-10-07
SE8700411L (en) 1987-10-29
DK216687A (en) 1987-10-29
NL8700352A (en) 1987-11-16
DK216687D0 (en) 1987-04-28
IT1202568B (en) 1989-02-09
JPS62254824A (en) 1987-11-06
AT395683B (en) 1993-02-25
ATA103187A (en) 1992-07-15

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