JPS6153102B2 - - Google Patents
Info
- Publication number
- JPS6153102B2 JPS6153102B2 JP53120100A JP12010078A JPS6153102B2 JP S6153102 B2 JPS6153102 B2 JP S6153102B2 JP 53120100 A JP53120100 A JP 53120100A JP 12010078 A JP12010078 A JP 12010078A JP S6153102 B2 JPS6153102 B2 JP S6153102B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- picric acid
- tar
- tower
- water
- 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
Links
- 239000007789 gas Substances 0.000 claims description 22
- OXNIZHLAWKMVMX-UHFFFAOYSA-N picric acid Chemical compound OC1=C([N+]([O-])=O)C=C([N+]([O-])=O)C=C1[N+]([O-])=O OXNIZHLAWKMVMX-UHFFFAOYSA-N 0.000 claims description 18
- 239000002351 wastewater Substances 0.000 claims description 13
- 238000000034 method Methods 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- LELOWRISYMNNSU-UHFFFAOYSA-N hydrogen cyanide Chemical compound N#C LELOWRISYMNNSU-UHFFFAOYSA-N 0.000 claims description 10
- 239000012535 impurity Substances 0.000 claims description 9
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 4
- 238000004140 cleaning Methods 0.000 claims description 4
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 4
- 239000003054 catalyst Substances 0.000 claims description 3
- 239000007864 aqueous solution Substances 0.000 claims 1
- 239000011269 tar Substances 0.000 description 17
- 239000007788 liquid Substances 0.000 description 12
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 10
- 238000006477 desulfuration reaction Methods 0.000 description 10
- 230000023556 desulfurization Effects 0.000 description 10
- 238000004821 distillation Methods 0.000 description 10
- 238000010521 absorption reaction Methods 0.000 description 6
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 238000000746 purification Methods 0.000 description 5
- 230000008929 regeneration Effects 0.000 description 5
- 238000011069 regeneration method Methods 0.000 description 5
- 238000004090 dissolution Methods 0.000 description 4
- 238000001704 evaporation Methods 0.000 description 4
- 230000008020 evaporation Effects 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 239000008235 industrial water Substances 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- 239000011593 sulfur Substances 0.000 description 3
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 2
- UFWIBTONFRDIAS-UHFFFAOYSA-N Naphthalene Chemical compound C1=CC=CC2=CC=CC=C21 UFWIBTONFRDIAS-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- ZMZDMBWJUHKJPS-UHFFFAOYSA-M Thiocyanate anion Chemical compound [S-]C#N ZMZDMBWJUHKJPS-UHFFFAOYSA-M 0.000 description 2
- 238000003763 carbonization Methods 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 239000011280 coal tar Substances 0.000 description 2
- 239000000571 coke Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- NJYFRQQXXXRJHK-UHFFFAOYSA-N (4-aminophenyl) thiocyanate Chemical compound NC1=CC=C(SC#N)C=C1 NJYFRQQXXXRJHK-UHFFFAOYSA-N 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- XYXNTHIYBIDHGM-UHFFFAOYSA-N ammonium thiosulfate Chemical compound [NH4+].[NH4+].[O-]S([O-])(=O)=S XYXNTHIYBIDHGM-UHFFFAOYSA-N 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 239000003034 coal gas Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000002250 progressing effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
Description
本発明は不純物を含有するガスの精製方法に関
する。特に不純物として硫化水素およびシアン化
水素等を含有するガスの精製方法に関する。
いま石炭乾留ガスを例とすれば、ガス中の不純
物としては硫化水素、シアン化水素およびアンモ
ニアならびタール分等があり、これらは精製して
除去する必要がある。これらの不純物の除去法と
して、特許第827210号(特公昭47−47561号)に
よれば、ガス中の有害成分である硫化水素、シア
ン化水素を有効に反応せしめることによつてロダ
ン化物を生成し、有害成分の無害化が達成され
る。このとき、ピクリン酸等の触媒が脱硫後の再
生反応の遂行に寄与し、硫黄の単離とその後のロ
ダン化反応の進行に関与することが知られてい
る。しかし、触媒としてピクリン酸を用いるとき
にはピクリン酸がきわめて冷水に難溶性のため、
少量ずつ溶解せしめなければならないという作業
上の難点があつた。ピクリン酸の水に対する溶解
度は1.2g/100g程度にすぎないからである。
石炭乾留ガスの精製系統の一例を第1図に示せ
ば、コークス炉1より乾留された粗ガス中のター
ル分はガス液とともに、先ず、デカンター2に集
められる。ついで、ガスは間接式冷縮器3で冷却
を受け、冷却されたタール分はタールピツト4に
集められる。その後、ガスはタール排除器5、排
送機6を経て、脱シアン塔7、脱硫塔8にて脱
硫、脱シアンを受ける。更に、アンモニア洗浄塔
10によつて余分のアンモニアは除去され、ナフ
タリン洗浄塔11を経て、ベンゾール吸収塔12
でベンゾールが吸収分離され、ガスはその後、フ
アイナルスクラバー13を経て乾式脱硫器14に
よつて処理を受け、ガスの精製が完成する。な
お、9は再生塔であり、脱シアン化塔7、脱硫塔
8での洗浄液は汚液槽15を経て再生塔に送られ
る。汚液槽からの液の一部は遠心分離機17で硫
黄を分離した後汚液槽15に循還するが、ピクリ
ン酸はピクリン酸溶解槽16にて水に溶解して、
汚液槽15に補給される。問題はピクリン酸溶解
槽16におけるピクリン酸の溶解にあつた。
第2図には間接式冷縮器等で冷却分離されたコ
ールタールの処理工程を示す。コールタールは1
8より供給され、熱交換器19,20を経て加圧
脱水器21に入る。加圧脱水器21で脱水を受け
た後は蒸発塔22に供給され、頂部よりの留出油
は油水分離器23でタール軽油と水に分離され
る。蒸発塔22の塔底油は加熱炉24にて加熱さ
れ、常圧精留塔25に供給され、頂部よりの留出
油は19で冷却された後、油水分離器27でタール
軽油と水に分離される。常圧精留塔25の塔底油
は一部、加圧脱水器21よりの油分と合し、又、
一部は加熱炉24に送られる。加熱炉24で加熱
を受けた後は減圧精留塔26に入り、頂部は真空
ポンプに連結して減圧を受けつつ、塔底からは熱
交換器20を経て中ピツチが取り出される。とこ
ろで23,27よりの分離排水はシアン化合物が
多く、到底このままでは放流できない。そこで油
水分離、活性汚泥処理、凝集沈澱、薬剤酸化処理
等の工程を経なければならず、設備費とランニン
グコストに相当な出費が必要であつた。該排水の
代表的な成分は第1表に示すとおりである。
The present invention relates to a method for purifying gas containing impurities. In particular, it relates to a method for purifying gas containing impurities such as hydrogen sulfide and hydrogen cyanide. Taking carbonized coal gas as an example, impurities in the gas include hydrogen sulfide, hydrogen cyanide, ammonia, and tar, which must be purified and removed. As a method for removing these impurities, according to Patent No. 827210 (Special Publication No. 47-47561), rhodanide is generated by effectively reacting hydrogen sulfide and hydrogen cyanide, which are harmful components in the gas. Harmful components are rendered harmless. At this time, it is known that a catalyst such as picric acid contributes to the regeneration reaction after desulfurization and is involved in the isolation of sulfur and the subsequent progression of the rhodanization reaction. However, when using picric acid as a catalyst, because picric acid is extremely poorly soluble in cold water,
There was a problem in the process that it had to be dissolved in small quantities. This is because the solubility of picric acid in water is only about 1.2g/100g. An example of a coal carbonization gas purification system is shown in FIG. 1. Tar in the crude gas carbonized from a coke oven 1 is first collected in a decanter 2 together with the gas liquid. The gas is then cooled in an indirect condenser 3, and the cooled tar is collected in a tar pit 4. Thereafter, the gas passes through a tar remover 5 and a discharger 6, and then undergoes desulfurization and decyanization in a desulfurization tower 7 and a desulfurization tower 8. Further, excess ammonia is removed by an ammonia washing tower 10, passed through a naphthalene washing tower 11, and then transferred to a benzol absorption tower 12.
Benzol is absorbed and separated, and the gas then passes through a final scrubber 13 and is treated by a dry desulfurizer 14, completing gas purification. Note that 9 is a regeneration tower, and the cleaning liquid from the desyanation tower 7 and the desulfurization tower 8 is sent to the regeneration tower via a waste liquid tank 15. A part of the liquid from the sewage tank is circulated to the sewage tank 15 after separating sulfur in a centrifuge 17, but picric acid is dissolved in water in a picric acid dissolving tank 16.
The waste liquid tank 15 is replenished. The problem was the dissolution of picric acid in the picric acid dissolution tank 16. Figure 2 shows the treatment process for coal tar that has been cooled and separated using an indirect condenser or the like. coal tar is 1
8 and enters the pressure dehydrator 21 via heat exchangers 19 and 20. After being dehydrated in a pressure dehydrator 21, it is supplied to an evaporation column 22, and the distillate from the top is separated into tar gas oil and water in an oil-water separator 23. The bottom oil of the evaporation tower 22 is heated in the heating furnace 24 and supplied to the atmospheric rectification tower 25, and the distilled oil from the top is cooled in 19, and then separated into tar gas oil and water in the oil-water separator 27. separated. A part of the bottom oil of the atmospheric rectification column 25 is combined with the oil from the pressure dehydrator 21, and
A portion is sent to the heating furnace 24. After being heated in the heating furnace 24, it enters a vacuum rectification column 26, the top of which is connected to a vacuum pump and subjected to reduced pressure, while the middle pitcher is taken out from the bottom of the column via a heat exchanger 20. By the way, the separated waste water from ports 23 and 27 contains a lot of cyanide, and cannot be discharged as is. Therefore, processes such as oil/water separation, activated sludge treatment, coagulation sedimentation, and chemical oxidation treatment had to be carried out, which required considerable expense in terms of equipment costs and running costs. Typical components of the wastewater are shown in Table 1.
【表】
本発明者は、一方ではガス精製用に必要とする
ピクリン酸の溶解が容易ではなく、長時間と多大
の手間を要するという難点の解決を迫られ、他方
ではタール蒸留排水の外部放流処理に多大な設備
を要するという苦難に際会して検討を重ねたので
あるが、これら両難点を一挙に解決できるすぐれ
た方法を見出すに至つた。
先ず、第2表に示すように、一定量の工業用水
とタール蒸留排水を対象として、一定量のピクリ
ン酸を同条件で投入し、すべて溶解するまでの時
間を測定比較したところ、顕著な差があることを
見出した。また、0.3%のピクリン酸を添加した
工業用水を使用した吸収液と、タール蒸留排水を
使用した吸収液について、粗石炭乾留ガスを同条
件で流した後に空気を吹込んで再生せしめた比[Table] On the one hand, the inventor was forced to solve the problem that picric acid, which is required for gas purification, is not easy to dissolve and requires a long time and a great deal of effort. We faced the challenge of requiring a large amount of equipment for treatment, and after much deliberation, we finally discovered an excellent method that could solve both of these problems at once. First, as shown in Table 2, when a certain amount of picric acid was added under the same conditions to a certain amount of industrial water and tar distillation wastewater, and the time required for it to completely dissolve was measured and compared, there was a noticeable difference. I found out that there is. In addition, we compared the absorption liquid using industrial water with 0.3% picric acid added and the absorption liquid using tar distillation wastewater, which were regenerated by blowing air after flowing crude coal carbonization gas under the same conditions.
【表】
較試験10回の平均は、第3表に示すように脱硫効
果にも明らかな差があることが知られた。タール
蒸留排水をいたものの方が吸収液中の硫黄分が高
く、またピクリン酸の活性が不十分な場合に生ず
るチオ硫酸アンモンは少い。更に蒸留排水の方が
シアン化水素の吸収効率もよく、ロダン化反応も
進んでいる。すなわち、通常行なわれている工業
用水を使用した吸収液に代えて、タール蒸留排水
を使用した方が、脱硫、脱シアンともに良結果が
得られることを確認するに至つた。[Table] As shown in Table 3, it was found that there was a clear difference in the desulfurization effect based on the average of 10 comparison tests. The sulfur content in the absorbent is higher when using tar distillation wastewater, and less ammonium thiosulfate is produced when the activity of picric acid is insufficient. Furthermore, distillation wastewater has better absorption efficiency of hydrogen cyanide, and the rhodanization reaction is also progressing. In other words, it has been confirmed that better results can be obtained in both desulfurization and decyanization by using tar distillation wastewater instead of the commonly used absorption liquid using industrial water.
【表】
本発明の実施方法としては、たとえば蒸発塔2
2又は常圧精留塔25よりの留出分ラインに油水
分離器23,27を設け、その水層よりの排水は
ストレーナを経てクツシヨンタンクに貯留し、そ
の後、撹拌器等を附属したピクリン酸溶解槽16
にまで導いたライン通じて、移送ポンプによつて
液を送り出せば、タール蒸留によつて生ずる排水
は全く外部に排出することなく、すべてピクリン
酸の溶解用に用いられる。その後、ピクリン酸溶
液が汚液槽15を経て再生塔9に送られ、液の再
生後ガスの精製工程に利用されることとなる。タ
ール蒸留排水がアンモニアアルカリ性であるた
め、ピクリン酸の溶解にきわめて有利であるとと
もに、タール蒸留排水に含有されるシアン分はロ
ダン化物に固定される。更にガス中の有害成分と
して存在するアンモニアを利用するときには、ロ
ダンアンモンとして固定することができ、これら
固定不純物を含有する廃液は濃縮後燃焼処理によ
つて硫酸又は硫酸塩として資源の再利用をはかる
ことができる(特公昭52−3404号)ので、本発明
は脱硫、脱シアン工程の合理化と、タール蒸留排
水の無害化にすぐれた相乗効果を奏するものであ
る。[Table] As a method of implementing the present invention, for example, evaporation tower 2
Oil-water separators 23 and 27 are installed in the distillate line from 2 or the atmospheric rectification column 25, and the waste water from the aqueous layer is stored in a cushion tank via a strainer. Acid dissolution tank 16
If the liquid is sent out by a transfer pump through a line led to the tank, the waste water generated by tar distillation will not be discharged to the outside and will be used entirely for dissolving the picric acid. Thereafter, the picric acid solution is sent to the regeneration tower 9 via the waste liquid tank 15, and after the liquid is regenerated, it is used in the gas purification process. Since tar distillation wastewater is ammonia alkaline, it is extremely advantageous for dissolving picric acid, and the cyanide contained in tar distillation wastewater is fixed in rhodanide. Furthermore, when ammonia, which exists as a harmful component in gas, is used, it can be fixed as rhodan ammonium, and the waste liquid containing these fixed impurities is recycled as sulfuric acid or sulfate through combustion treatment after concentration. (Japanese Patent Publication No. 52-3404) Therefore, the present invention has an excellent synergistic effect in streamlining the desulfurization and decyanization steps and in making tar distillation wastewater harmless.
第1図は不純物を含有するガスの精製工程全体
を例示する系統図であり、第2図はタール蒸留設
備を例示する系統図である。
1……コークス炉、2……デカンター、3……
冷縮器、4……タールピツト、7……脱シアン
塔、8……脱硫塔、9……再生塔、12……ベン
ゾール吸収塔、15……汚液槽、16……ピクリ
ン酸溶解槽、22……蒸発塔、25……常圧精留
塔、23,27……油水分離器。
FIG. 1 is a system diagram illustrating the entire purification process for gas containing impurities, and FIG. 2 is a system diagram illustrating tar distillation equipment. 1...Coke oven, 2...Decanter, 3...
Condenser, 4... Tar pit, 7... Desulfurization tower, 8... Desulfurization tower, 9... Regeneration tower, 12... Benzol absorption tower, 15... Sewage tank, 16... Picric acid dissolution tank, 22...Evaporation column, 25...Normal pressure rectification column, 23, 27...Oil-water separator.
Claims (1)
を含有するガスに対して、ピクリン酸を触媒とし
た水溶液でガスを洗浄して精製する工程におい
て、ガス中の他の不純物であるタール分を冷却分
離して蒸留する際に生ずる蒸留排水を、ピクリン
酸を溶解してガスを洗浄すべき洗浄用水として用
いる、不純物を含有するガスの精製方法。1. In the process of cleaning and purifying gas containing impurities such as hydrogen sulfide and hydrogen cyanide with an aqueous solution using picric acid as a catalyst, other impurities in the gas, such as tar, are cooled and separated and then distilled. A method for purifying gas containing impurities, in which the distilled waste water produced during the process is used as cleaning water for dissolving picric acid and cleaning the gas.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12010078A JPS5547118A (en) | 1978-09-28 | 1978-09-28 | Purification of gas containing impurity |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP12010078A JPS5547118A (en) | 1978-09-28 | 1978-09-28 | Purification of gas containing impurity |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5547118A JPS5547118A (en) | 1980-04-03 |
JPS6153102B2 true JPS6153102B2 (en) | 1986-11-15 |
Family
ID=14777907
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP12010078A Granted JPS5547118A (en) | 1978-09-28 | 1978-09-28 | Purification of gas containing impurity |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5547118A (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100398421B1 (en) * | 1999-12-23 | 2003-09-19 | 주식회사 포스코 | A method for purification cog using chilling method |
KR100446648B1 (en) * | 2000-08-24 | 2004-09-04 | 주식회사 포스코 | Method for purifying coke oven gas by cooling down to freezing point of water |
CN101879398B (en) * | 2010-06-29 | 2012-06-27 | 南京钢铁股份有限公司 | Recovery process of coking crude benzene dispersing gas and device thereof |
CN102994171B (en) * | 2011-09-17 | 2014-09-17 | 河南利源煤焦集团有限公司 | Gas turbine generating coke oven gas comprehensive purification system and purification method thereof |
-
1978
- 1978-09-28 JP JP12010078A patent/JPS5547118A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS5547118A (en) | 1980-04-03 |
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