Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0159008B2 - - Google Patents
[go: Go Back, main page]

JPH0159008B2 - - Google Patents

Info

Publication number
JPH0159008B2
JPH0159008B2 JP57024461A JP2446182A JPH0159008B2 JP H0159008 B2 JPH0159008 B2 JP H0159008B2 JP 57024461 A JP57024461 A JP 57024461A JP 2446182 A JP2446182 A JP 2446182A JP H0159008 B2 JPH0159008 B2 JP H0159008B2
Authority
JP
Japan
Prior art keywords
halogen gas
strength
limestone
absorbent
gas
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
JP57024461A
Other languages
Japanese (ja)
Other versions
JPS58143837A (en
Inventor
Shiro Ida
Keiichiro Kiba
Kazuhiko Tsuji
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.)
Mitsui Mining Co Ltd
Original Assignee
Mitsui Mining Co Ltd
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 Mitsui Mining Co Ltd filed Critical Mitsui Mining Co Ltd
Priority to JP57024461A priority Critical patent/JPS58143837A/en
Publication of JPS58143837A publication Critical patent/JPS58143837A/en
Publication of JPH0159008B2 publication Critical patent/JPH0159008B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

Landscapes

  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Description

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

この発明は、人体、機械装置等を浸食するハロ
ゲンガスの吸収除去剤で、ハロゲンガス吸収後こ
れをそのまま放棄してもハロゲンガスの大気拡散
等の公害発生の恐れがなく、使用工程等取扱い過
程で粉化することが少ない強度を有するハロゲン
吸収剤に関するものである。 最近、燃焼排ガスの乾式脱硫脱硝に活性炭を用
いる工程が多く採用されている。SO2吸収後の活
性炭は再生工程で、いわゆるSO2リツチガスを脱
着するが、このリツチガス中には石炭燃焼の場合
で塩化水素0.5〜5V%程度、フツ化水素0.05〜1V
%程度、都市ゴミ燃焼の場合で塩化水素が時には
5V%以上も含まれている これらのSO2リツチガスに含まれている高濃度
のハロゲンガスは水蒸気等の水分存在下で装置浸
食の元凶となるばかりか、大気に放散すると公害
源となるので高度の除去が要求される。 ハロゲンガス吸収剤としてアルミナ、酸化第2
鉄、酸化チタン、アルカリ土類金属の酸化物等を
主成分とする組成物が開発出願されているが、
(特開昭56−163740)、これらの組成物はハロゲン
ガス吸収能においてなお不充分である。 本発明者らは、ハロゲンガス吸収剤の主成分と
して種々の化合物について研究の結果、消石灰が
最もハロゲンガス吸収能力に勝れていることを見
出した。消石灰は価格も安く経済的であるが、こ
れを成形したものは消石灰単味では衝撃等による
破砕紛化がおこり、吸収工程の流動層等でガス圧
の上昇等によりガス流を阻害したり、又ハロゲン
吸収後の吸収剤の放棄等の取扱いが困難になるな
どの問題点があつた。そこで、本発明者等は、消
石灰紛に石灰石粉を混合し成形することにより強
度を高めることが出来ることを見出し本ハロゲン
ガス吸収剤の発明に到つた。石灰石の混合により
ハロゲンガス吸収剤の強度が上昇し、石灰石混合
率30〜60wt%程度で最高値となるが、80wt%程
度までは強度上昇効果が認められる。しかしなが
ら、石灰石の混合率があまり高くなるとハロゲン
ガスの吸収能が低下する。従つて、混合率は両者
を勘案して適宜定めればよいが、通常は成形品の
60wt%以下、好ましくは10〜40wt%、さらに好
ましくは20〜35wt%混合するのがよい。 本発明のハロゲンガス吸収剤は例えば次のよう
にして製造する。 (1) 100メツシユ以下に微分砕した石灰石を900〜
1200℃で焼成し生石灰とした後、所定量の石灰
石紛及び生石灰と同重量程度の水を添加して混
練し、造粒に適するように水分量を調整して成
形機又は造粒機で粒の大きさ5〜15mm程度に成
形後100〜200℃の温度で乾燥して製造する。 (2) 通常市販されている消石灰紛に所定量の100
メツシユ以下に微紛砕した石灰石を混合し、造
粒に適するような量の水を加えて混練し、上記
(1)と同方法で成形乾燥して製造する。 なお、ハロゲンガス吸収剤の製造方法はこれら
の方法に限られるものではない。 こうして造つたハロゲンガス吸収剤は、ハロゲ
ンガス吸収後の強度が石灰石を混合しないものに
比較して著しく高く、ハロゲンガス吸収工程でガ
ス流を阻害することなく、又吸収後の吸収剤の取
扱いが容易である特徴を有する。 実施例によりハロゲンガス吸収剤の性状を説明
する。 実施例 100メツシユ以下に紛砕した石灰石4000gを
1000℃で1時間焼成し生石灰紛を得た。これを4
等分し、それぞれに水600g、100メツシユ以下に
紛砕した石灰石紛(以下石灰石紛と称す)130g
と水600g、石灰石紛400gと水600g、及び石灰
石紛1110gと水600gを加えて混練したもの、そ
れとは別に石灰石1000gに水600gを加え混練し
たものの5種に造粒に適するよう水を加えて調整
し、ドラム回転式造粒機で粒の大きさ5〜7mmの
ペレツトした後、これを150℃で2時間乾燥して、
各々730g、860g、1100g、1820g及び1000gの
ハロゲンガス吸収剤を造つた。 この5種のハロゲンガス吸収剤について、強度
試験及びハロゲンガス吸収量を測定した。 強度試験はJISM8801に示されているロガ試験
法を応用してロガ試験機を用いて行つた。すなわ
ち、回転ドラムにハロゲンガス吸収剤15gを入
れ、50回転/分の速さで1000回転した後、このハ
ロゲンガス吸収剤を篩目3mmと1.7mmの篩でふる
い、篩網上の重量の全試量重量に対する%をもつ
て>3mm強度、>1.7mm強度とした。 >3mm強度(%)=3mm篩上試料重量(g)/15(g
)× 100 >1.7mm強度(%)=1.7mm篩上試料重量(g)/15(
g) ×100 ハロゲンガス吸収能試験は、表1に示す組成を
もつSO2共存ガス、及びSO2不在ガスについて測
定した。
This invention is an absorbing and removing agent for halogen gas that corrodes the human body, machinery, etc., and even if it is discarded after absorbing halogen gas, there is no risk of pollution such as diffusion of halogen gas into the atmosphere, and there is no risk of pollution occurring during the use process and handling process. This invention relates to a halogen absorbent that has a strength that prevents it from pulverizing. Recently, processes using activated carbon have been widely adopted for dry desulfurization and denitration of combustion exhaust gas. The activated carbon after absorbing SO 2 desorbs so-called SO 2 rich gas in the regeneration process, but in the case of coal combustion, this rich gas contains about 0.5 to 5 V% of hydrogen chloride and 0.05 to 1 V of hydrogen fluoride.
%, hydrogen chloride is sometimes produced when municipal waste is incinerated.
The high concentration of halogen gas contained in these SO 2 rich gases not only causes equipment erosion in the presence of moisture such as water vapor, but also becomes a source of pollution when released into the atmosphere. is required to be removed. Alumina, secondary oxide as halogen gas absorbent
Applications have been filed for the development of compositions containing iron, titanium oxide, alkaline earth metal oxides, etc. as main components.
(Japanese Patent Application Laid-open No. 56-163740), these compositions are still insufficient in their ability to absorb halogen gas. As a result of research on various compounds as main components of halogen gas absorbents, the present inventors found that slaked lime has the best halogen gas absorption ability. Slaked lime is cheap and economical, but when molded from slaked lime alone, it can be crushed into powder due to impact, etc., and the gas flow may be obstructed due to increased gas pressure in the fluidized bed of the absorption process, etc. Further, there were other problems such as difficulty in handling, such as discarding the absorbent after absorbing the halogen. Therefore, the present inventors found that the strength could be increased by mixing limestone powder with slaked lime powder and molding the mixture, leading to the invention of the present halogen gas absorbent. The strength of the halogen gas absorbent increases with the addition of limestone, reaching a maximum value at a limestone mixing ratio of about 30 to 60 wt%, but the strength increasing effect is observed up to about 80 wt%. However, if the mixing ratio of limestone becomes too high, the ability to absorb halogen gas decreases. Therefore, the mixing ratio can be determined as appropriate by taking both factors into consideration, but usually it is
It is preferable to mix 60 wt% or less, preferably 10 to 40 wt%, more preferably 20 to 35 wt%. The halogen gas absorbent of the present invention is produced, for example, as follows. (1) Limestone finely crushed to 100 mesh or less
After baking at 1200℃ to make quicklime, add a predetermined amount of limestone powder and water of about the same weight as quicklime, knead it, adjust the moisture content to make it suitable for granulation, and granulate it with a molding machine or granulator. It is manufactured by molding it to a size of about 5 to 15 mm and drying it at a temperature of 100 to 200°C. (2) A predetermined amount of 100 ml of slaked lime powder commonly available on the market.
Mix finely pulverized limestone to less than mesh, add an amount of water suitable for granulation and knead, and then
Manufactured by molding and drying in the same manner as in (1). Note that the method for producing the halogen gas absorbent is not limited to these methods. The halogen gas absorbent produced in this way has significantly higher strength after absorbing halogen gas than one that does not contain limestone, does not impede gas flow during the halogen gas absorption process, and is easy to handle after absorption. It has the characteristic of being easy. The properties of the halogen gas absorbent will be explained using Examples. Example: 4000g of limestone crushed to less than 100 mesh
It was calcined at 1000°C for 1 hour to obtain quicklime powder. This is 4
Equally divided into 600 g of water and 130 g of limestone powder (hereinafter referred to as limestone powder) crushed to 100 mesh or less.
and 600g of water, 400g of limestone powder and 600g of water, 1110g of limestone powder and 600g of water and kneaded, and separately 1000g of limestone and 600g of water and kneaded.Water was added to make it suitable for granulation. After adjusting and making pellets with a particle size of 5 to 7 mm using a drum rotary granulator, this was dried at 150°C for 2 hours.
730g, 860g, 1100g, 1820g and 1000g of halogen gas absorbent were produced respectively. For these five types of halogen gas absorbents, strength tests and halogen gas absorption amounts were measured. The strength test was conducted using a loga tester using the loga test method specified in JISM8801. That is, 15 g of halogen gas absorbent is placed in a rotating drum, rotated 1000 times at a speed of 50 revolutions/minute, and then sieved through a sieve with mesh sizes of 3 mm and 1.7 mm to remove all of the weight on the sieve screen. The strength was defined as >3 mm strength and >1.7 mm strength as a percentage of the sample weight. >3mm strength (%) = sample weight on 3mm sieve (g) / 15 (g
) × 100 >1.7mm strength (%) = sample weight on 1.7mm sieve (g) / 15 (
g) ×100 The halogen gas absorption capacity test was performed on SO 2 coexisting gases and SO 2 absent gases having the compositions shown in Table 1.

【表】 ハロゲンガス吸収剤16gを300℃雰囲気の吸収
管に置き、試料ガスを260ml/minで通じ、吸収
管出口で水酸化ナトリウム溶液に残余のハロゲン
ガスを吸収させ、吸収管出口濃度を測定し、脱
HCl率90%以上を維持する時間及びその時のHCl
ガス吸収量(HClg/吸収剤g)を測定した。 ハロゲンガス吸収剤の強度及び吸収能試験結果
を表2に示した。
[Table] Place 16g of halogen gas absorbent in an absorption tube in a 300℃ atmosphere, pass the sample gas at 260ml/min, let the sodium hydroxide solution absorb the remaining halogen gas at the absorption tube outlet, and measure the concentration at the absorption tube outlet. And get off
Time to maintain HCl rate of 90% or more and HCl at that time
The amount of gas absorbed (HClg/g absorbent) was measured. Table 2 shows the strength and absorption capacity test results of the halogen gas absorbent.

【表】 比較試験例 比較試験試料として、西独製ハロゲンガス吸収
剤(石灰主体、市販品)を実施例と同様の強度試
験及びHCl吸収能試験を行なつた。その結表は表
3に示す。
[Table] Comparative Test Example As a comparative test sample, a halogen gas absorbent made in West Germany (mainly lime, commercially available) was subjected to the same strength test and HCl absorption capacity test as in the example. The results are shown in Table 3.

【表】 表3に示したように市販品のハロゲンガス吸収
剤に比較して、本発明品はハロゲンガス吸収前後
共強度が高く、ガス圧の上昇等よる弊害がなく、
使用上の取扱い易さで各段の進歩がある発明であ
る。
[Table] As shown in Table 3, compared to commercially available halogen gas absorbents, the product of the present invention has higher strength both before and after absorbing halogen gas, and has no adverse effects such as increases in gas pressure.
This is an invention that has made great strides in terms of ease of use and handling.

Claims (1)

【特許請求の範囲】[Claims] 1 消石灰に石灰石を混合し、ペレツト状に成形
したハロゲンガス吸収剤。
1. A halogen gas absorbent made by mixing slaked lime with limestone and forming it into pellets.
JP57024461A 1982-02-19 1982-02-19 Absorbent for halogen gas Granted JPS58143837A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57024461A JPS58143837A (en) 1982-02-19 1982-02-19 Absorbent for halogen gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57024461A JPS58143837A (en) 1982-02-19 1982-02-19 Absorbent for halogen gas

Publications (2)

Publication Number Publication Date
JPS58143837A JPS58143837A (en) 1983-08-26
JPH0159008B2 true JPH0159008B2 (en) 1989-12-14

Family

ID=12138801

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57024461A Granted JPS58143837A (en) 1982-02-19 1982-02-19 Absorbent for halogen gas

Country Status (1)

Country Link
JP (1) JPS58143837A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08108039A (en) * 1994-10-11 1996-04-30 Netsushii Kogyo Kk Exhaust gas treating device
JP5170040B2 (en) * 2009-09-01 2013-03-27 株式会社日立製作所 HF-containing gas dry processing apparatus and processing method

Also Published As

Publication number Publication date
JPS58143837A (en) 1983-08-26

Similar Documents

Publication Publication Date Title
JP5740070B2 (en) Adsorbent to remove mercury from flue gas
US4786484A (en) Process for absorbing toxic gas
US4721582A (en) Toxic gas absorbent and processes for making same
JPH09508855A (en) Absorbent
US5360468A (en) Sulfur absorbents
TW201829049A (en) Agent for removing halogen gas, method for producing same, method for removing halogen gas with use of same, and system for removing halogen gas
JP4913271B2 (en) Halogen gas treatment agent
JPH0159008B2 (en)
JP3571095B2 (en) Method for producing acid gas absorbent
EP2217543A1 (en) Activated carbon as mercury release control agent in gypsum calcination
US3663457A (en) Method of preparing an oxidizing catalyst for the exhaust gases of internal combustion engines
HK174095A (en) Agents and method for purifying gases and waste gases from heavy metals, and method of producing these agents
WO2004078374A1 (en) Soil conditioner
JPH044015B2 (en)
KR100333184B1 (en) Preparing method of an absorbent for sulfur oxide in low temperature.
JPH11197445A (en) Exhaust gas treatment agent and its preparation
JPS61293546A (en) Acidic gas removing agent
JPH01284324A (en) Method for simultaneously removing sulfur oxide and nitrogen oxide
DE2924585A1 (en) Solid absorbent for dry dehalogenation of gas stream - consists of moulded calcium hydroxide contg. basic calcium sulphite
CN103495402A (en) Modified activated carbon absorb based desulfurizer for absorbing ultraviolet ray and its preparation method
JP3985291B2 (en) Method for removing mercury from flue gas
JPS6229092B2 (en)
JP2004073974A (en) Halogen gas removing agent and method for producing the same
JPH0421537B2 (en)
JPH0372914A (en) Method for treatment of exhaust gas and preparation of silica gel utilizing the same