JPS6015758B2 - Improved methods for chemical recovery in paper mills - Google Patents
Improved methods for chemical recovery in paper millsInfo
- Publication number
- JPS6015758B2 JPS6015758B2 JP51122913A JP12291376A JPS6015758B2 JP S6015758 B2 JPS6015758 B2 JP S6015758B2 JP 51122913 A JP51122913 A JP 51122913A JP 12291376 A JP12291376 A JP 12291376A JP S6015758 B2 JPS6015758 B2 JP S6015758B2
- Authority
- JP
- Japan
- Prior art keywords
- hydrogen sulfide
- dioxide gas
- liquid
- sulfur dioxide
- sodium
- 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
- 238000011084 recovery Methods 0.000 title claims description 30
- 238000000034 method Methods 0.000 title claims description 26
- 239000000126 substance Substances 0.000 title claims description 25
- 239000007789 gas Substances 0.000 claims description 57
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 51
- 238000010521 absorption reaction Methods 0.000 claims description 46
- 239000007788 liquid Substances 0.000 claims description 45
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 37
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 37
- CDBYLPFSWZWCQE-UHFFFAOYSA-L sodium carbonate Substances [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 28
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 18
- 239000003054 catalyst Substances 0.000 claims description 13
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 claims description 12
- 239000007864 aqueous solution Substances 0.000 claims description 11
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 11
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 10
- 235000010265 sodium sulphite Nutrition 0.000 claims description 6
- 229910052742 iron Inorganic materials 0.000 claims description 5
- 150000002696 manganese Chemical class 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 3
- 150000002500 ions Chemical class 0.000 claims 1
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 16
- 230000000694 effects Effects 0.000 description 12
- 235000017550 sodium carbonate Nutrition 0.000 description 10
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 8
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 8
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 8
- 239000001569 carbon dioxide Substances 0.000 description 8
- 229910002092 carbon dioxide Inorganic materials 0.000 description 8
- 229910052708 sodium Inorganic materials 0.000 description 8
- 239000011734 sodium Substances 0.000 description 8
- 229910052717 sulfur Inorganic materials 0.000 description 8
- 239000011593 sulfur Substances 0.000 description 8
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 7
- 238000009993 causticizing Methods 0.000 description 7
- 239000003513 alkali Substances 0.000 description 6
- 235000011121 sodium hydroxide Nutrition 0.000 description 5
- 239000000292 calcium oxide Substances 0.000 description 4
- 235000012255 calcium oxide Nutrition 0.000 description 4
- 238000010411 cooking Methods 0.000 description 4
- 230000007423 decrease Effects 0.000 description 4
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 238000007254 oxidation reaction Methods 0.000 description 4
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 3
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 3
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 3
- 241001062472 Stokellia anisodon Species 0.000 description 3
- 235000011941 Tilia x europaea Nutrition 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 239000004571 lime Substances 0.000 description 3
- 239000011572 manganese Substances 0.000 description 3
- 229910052748 manganese Inorganic materials 0.000 description 3
- 229940099596 manganese sulfate Drugs 0.000 description 3
- 239000011702 manganese sulphate Substances 0.000 description 3
- 235000007079 manganese sulphate Nutrition 0.000 description 3
- SQQMAOCOWKFBNP-UHFFFAOYSA-L manganese(II) sulfate Chemical compound [Mn+2].[O-]S([O-])(=O)=O SQQMAOCOWKFBNP-UHFFFAOYSA-L 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 239000000123 paper Substances 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000011790 ferrous sulphate Substances 0.000 description 2
- 235000003891 ferrous sulphate Nutrition 0.000 description 2
- 229910000358 iron sulfate Inorganic materials 0.000 description 2
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 2
- 239000002655 kraft paper Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 229910052938 sodium sulfate Inorganic materials 0.000 description 2
- 235000011152 sodium sulphate Nutrition 0.000 description 2
- AKHNMLFCWUSKQB-UHFFFAOYSA-L sodium thiosulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=S AKHNMLFCWUSKQB-UHFFFAOYSA-L 0.000 description 2
- 235000019345 sodium thiosulphate Nutrition 0.000 description 2
- 238000010025 steaming Methods 0.000 description 2
- 150000004763 sulfides Chemical class 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 241000207199 Citrus Species 0.000 description 1
- 229910021380 Manganese Chloride Inorganic materials 0.000 description 1
- GLFNIEUTAYBVOC-UHFFFAOYSA-L Manganese chloride Chemical compound Cl[Mn]Cl GLFNIEUTAYBVOC-UHFFFAOYSA-L 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 238000001311 chemical methods and process Methods 0.000 description 1
- 235000020971 citrus fruits Nutrition 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- IMBKASBLAKCLEM-UHFFFAOYSA-L ferrous ammonium sulfate (anhydrous) Chemical compound [NH4+].[NH4+].[Fe+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O IMBKASBLAKCLEM-UHFFFAOYSA-L 0.000 description 1
- RAQDACVRFCEPDA-UHFFFAOYSA-L ferrous carbonate Chemical compound [Fe+2].[O-]C([O-])=O RAQDACVRFCEPDA-UHFFFAOYSA-L 0.000 description 1
- 239000000796 flavoring agent Substances 0.000 description 1
- 235000019634 flavors Nutrition 0.000 description 1
- CPSYWNLKRDURMG-UHFFFAOYSA-L hydron;manganese(2+);phosphate Chemical compound [Mn+2].OP([O-])([O-])=O CPSYWNLKRDURMG-UHFFFAOYSA-L 0.000 description 1
- 150000002505 iron Chemical class 0.000 description 1
- FBAFATDZDUQKNH-UHFFFAOYSA-M iron chloride Chemical compound [Cl-].[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-M 0.000 description 1
- 235000014413 iron hydroxide Nutrition 0.000 description 1
- 229910000398 iron phosphate Inorganic materials 0.000 description 1
- 159000000014 iron salts Chemical class 0.000 description 1
- MVFCKEFYUDZOCX-UHFFFAOYSA-N iron(2+);dinitrate Chemical compound [Fe+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MVFCKEFYUDZOCX-UHFFFAOYSA-N 0.000 description 1
- WBJZTOZJJYAKHQ-UHFFFAOYSA-K iron(3+) phosphate Chemical compound [Fe+3].[O-]P([O-])([O-])=O WBJZTOZJJYAKHQ-UHFFFAOYSA-K 0.000 description 1
- PVFSDGKDKFSOTB-UHFFFAOYSA-K iron(3+);triacetate Chemical compound [Fe+3].CC([O-])=O.CC([O-])=O.CC([O-])=O PVFSDGKDKFSOTB-UHFFFAOYSA-K 0.000 description 1
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 1
- 239000011565 manganese chloride Substances 0.000 description 1
- 235000002867 manganese chloride Nutrition 0.000 description 1
- 229940099607 manganese chloride Drugs 0.000 description 1
- 150000002697 manganese compounds Chemical class 0.000 description 1
- IPJKJLXEVHOKSE-UHFFFAOYSA-L manganese dihydroxide Chemical compound [OH-].[OH-].[Mn+2] IPJKJLXEVHOKSE-UHFFFAOYSA-L 0.000 description 1
- MIVBAHRSNUNMPP-UHFFFAOYSA-N manganese(2+);dinitrate Chemical compound [Mn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MIVBAHRSNUNMPP-UHFFFAOYSA-N 0.000 description 1
- 239000000155 melt Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N nitrogen Substances N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 229910052979 sodium sulfide Inorganic materials 0.000 description 1
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 1
- 238000005486 sulfidation Methods 0.000 description 1
- 235000010269 sulphur dioxide Nutrition 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Paper (AREA)
Description
【発明の詳細な説明】
従来、ガス中の硫化水素を吸収するためには、pHIO
以上のアルカリ水溶液が用いられる。[Detailed Description of the Invention] Conventionally, in order to absorb hydrogen sulfide in gas, pHIO
The above alkaline aqueous solutions are used.
そして、この液を硫化水素吸収に用いることは当然考え
られ、吸収効果も充分であることは明らかである。しか
し、硫化水素吸収液として循環使用すると液中に硫化物
が蓄積され、次第に硫化水素吸収効果が落ちてくる。し
たがって継続して硫化素の吸収効果を保たせるためには
、何らかの方法で液中の硫化物を除く必要がある。その
方法として、硫化物を空気酸化させて液中の硫化物濃度
を下げることが考えられるが、それには当然大きな酸化
設備が必要となる。さらに、対10以上のアルカリ液を
使う場合には、排ガス中に含まれる相当量の炭酸ガスが
アルカリを消費し、経済的にも好ましくない。It is natural that this liquid can be used to absorb hydrogen sulfide, and it is clear that the absorption effect is sufficient. However, when used repeatedly as a hydrogen sulfide absorption liquid, sulfide accumulates in the liquid, and the hydrogen sulfide absorption effect gradually decreases. Therefore, in order to maintain the sulfide absorption effect continuously, it is necessary to remove sulfide from the liquid by some method. One possible method for this is to reduce the sulfide concentration in the liquid by oxidizing the sulfide in the air, but this naturally requires large oxidation equipment. Furthermore, when using an alkali solution with a ratio of 10 or more, a considerable amount of carbon dioxide gas contained in the exhaust gas consumes the alkali, which is not economically preferable.
舟9以下であれば、炭酸ガスを吸収することはないが、
硫化水素の吸収は50〜40%以下となってしまう。し
かし、本方法では、微量の硫酸鉄、硫酸マンガン等の鉄
塩、マンガン塩の塩類を単独に、又は上記の塩類を混合
して触媒として添加するだけで、大きな酸化設備を必要
とせず、しかもpHIo以下の領域で、炭酸ガスの影響
を受けず、選択的に硫化水素及び亜硫酸ガスを吸収する
ことができる。吸収液として用いるアルカリ性水溶液は
軸の高い領域では炭酸ガスを吸収し、そのため、掛値が
下がるが、やがてガス中の炭酸ガス分圧と平衡の液組成
になるとそれ以上の炭酸ガスの吸収は起こらず、炭酸ガ
スによる柑の低下はみられなくなる。If the boat is below 9, it will not absorb carbon dioxide gas, but
The absorption of hydrogen sulfide ends up being less than 50-40%. However, in this method, only a trace amount of iron salts such as iron sulfate and manganese sulfate, or manganese salts are added alone or in a mixture of the above salts as a catalyst, and large oxidation equipment is not required. Hydrogen sulfide and sulfur dioxide gas can be selectively absorbed in the range below pHIo without being affected by carbon dioxide gas. The alkaline aqueous solution used as the absorption liquid absorbs carbon dioxide gas in the region with a high axis, and as a result, the multiplier value decreases, but eventually, when the liquid composition reaches equilibrium with the partial pressure of carbon dioxide gas in the gas, no further absorption of carbon dioxide gas occurs. First, the deterioration of citrus flavor due to carbon dioxide gas is no longer observed.
この班低下の停止額向はpHIO以下から始まり、舟9
前後で落ち着く。また、掛値8.3以下になると、液中
より炭酸ガスが発生し始める。したがって、硫化水素及
び亜硫酸ガスを吸収除去する吸収液としてアルカリ性水
溶液を用いる場合の餌領域は8.3〜斑10.0とする
のが望ましい。また、吸収液濃度は高い程硫化水素及び
亜硫酸ガスの吸収効果が良いが、炭酸ナトリウム換算と
して2重量%以上で吸収効果があった。さらに、吸収液
温度は20qo〜95℃で、硫化水素及び亜硫酸ガスの
吸収効果がよかった。以上のpH、濃度、温度条件下で
前記触媒の添加により、硫化水素及び亜硫酸ガスの高い
吸収効果を得た。The stop value of this group decrease starts from below pHIO, and boat 9
Calm before and after. Further, when the multiplication value becomes 8.3 or less, carbon dioxide gas starts to be generated from the liquid. Therefore, when using an alkaline aqueous solution as an absorbing liquid for absorbing and removing hydrogen sulfide and sulfur dioxide gas, it is desirable that the bait range be 8.3 to 10.0. Furthermore, the higher the concentration of the absorption liquid, the better the absorption effect of hydrogen sulfide and sulfur dioxide gas, but the absorption effect was found at 2% by weight or more in terms of sodium carbonate. Furthermore, the absorption liquid temperature was 20qo to 95°C, and the absorption effect of hydrogen sulfide and sulfur dioxide gas was good. By adding the catalyst under the above pH, concentration, and temperature conditions, a high absorption effect of hydrogen sulfide and sulfur dioxide gas was obtained.
触媒としての各種金属塩は徴量で良く、30の9′そ以
下でも充分な吸収効果を発揮する。鉄塩、マンガン塩、
としては、硫酸鉄、塩化鉄、硝酸鉄、水酸化鉄、炭酸鉄
、リン酸鉄、酢酸鉄、硫酸鉄アンモニウム、鉄キレ−ト
化合物及び硫酸マンガン、塩化マンガン、硝酸マンガン
、水酸化マンガン、炭酸マンガン、リン酸マンガン等の
鉄、マンガンの各化合物を使用することができる。ガス
中の硫化水素の濃度が低く、吸収液に化物として固定さ
れる量が少ない場合は、吸収液が吸収塔を通過する間に
、ガス中の酸素と鉄、マンガン等の触媒により液中硫化
物が速やかに酸化され、液中の硫化物が処理されるため
、ガス中の硫化水素、亜硫酸ガスの吸収除去効果は持続
する。しかし、ガス中の硫化水素濃度が高くなると、ガ
ス中の酸素量だけでは吸収液に固定された硫化物を処理
できずに、鉄、マンガン等の硫化物が生じ、吸収液から
の硫化水素の発生がみられ、ガス中の硫化水素・吸収効
果が悪くなる場合もある。亜硫酸ガスは、この状態でも
pHが前述の条件を維持していれば、吸収効果は変わり
なく持続する。ガス中の硫化水素濃度が高くなって、吸
収液からの硫化水素の発生、ガス中の硫化水素吸収効果
の低下が生じた場合でも、ガス中の酸素濃度を増加させ
るか、吸収液の簡単な空気酸化をすることによって、液
中の硫化物を処理することができる。もちろんこの場合
においても、吸収液中に前記触媒が存在することが必要
であり、触媒が無いと酸化装置が大きくなり、また逆に
空気により吸収液中からの硫化水素の発生を促す結果と
もなる。本発明は、以上の諸条件下で硫化水素及び亜硫
酸ガスを効率よく吸収する際に、硫化水素及び亜硫酸ガ
スの吸収により消費されたアルカリの補給用アルカリと
して、水酸化ナトリウム、炭酸ナトリウム、亜硫酸ナト
リウム等のアルカリ水溶液を使用し、回収ポィラ等の製
紙工場薬品回収工程から生じる排ガスとして逃げる硫化
水素、亜硫酸ガスを吸収し、吸収した液は一部抜き出し
て薬品回収工程に戻し、該イオウ分を有効に回収する薬
品回収の改良方法である。Various metal salts used as catalysts may be used in small amounts, and even amounts of less than 309' can exhibit sufficient absorption effects. iron salt, manganese salt,
Examples include iron sulfate, iron chloride, iron nitrate, iron hydroxide, iron carbonate, iron phosphate, iron acetate, ammonium iron sulfate, iron chelate compounds, and manganese sulfate, manganese chloride, manganese nitrate, manganese hydroxide, carbonate. Iron and manganese compounds such as manganese and manganese phosphate can be used. If the concentration of hydrogen sulfide in the gas is low and the amount fixed as a compound in the absorption liquid is small, the oxygen in the gas and a catalyst such as iron or manganese will cause sulfidation in the liquid while the absorption liquid passes through the absorption tower. Since the substance is quickly oxidized and the sulfide in the liquid is treated, the effect of absorbing and removing hydrogen sulfide and sulfur dioxide gas in the gas continues. However, when the concentration of hydrogen sulfide in the gas increases, the amount of oxygen in the gas alone cannot treat the sulfide fixed in the absorption liquid, and sulfides such as iron and manganese are generated, causing hydrogen sulfide to be released from the absorption liquid. Occasionally, hydrogen sulfide in the gas may be generated and the absorption effect may deteriorate. Even in this state, the absorption effect of sulfur dioxide gas continues as long as the pH maintains the above-mentioned conditions. Even if the concentration of hydrogen sulfide in the gas increases, resulting in generation of hydrogen sulfide from the absorption liquid or a decrease in the hydrogen sulfide absorption effect in the gas, increase the oxygen concentration in the gas or simply remove the absorption liquid from the absorption liquid. Sulfides in the liquid can be treated by air oxidation. Of course, in this case as well, it is necessary for the catalyst to be present in the absorption liquid; without the catalyst, the oxidation device will become bulky, and conversely, air will promote the generation of hydrogen sulfide from the absorption liquid. . When efficiently absorbing hydrogen sulfide and sulfur dioxide gas under the above conditions, the present invention uses sodium hydroxide, sodium carbonate, and sodium sulfite as a replenishing alkali for the alkali consumed by the absorption of hydrogen sulfide and sulfur dioxide gas. Hydrogen sulfide and sulfur dioxide gas that escapes as exhaust gas generated from paper mill chemical recovery processes such as recovery pollers are absorbed using an alkaline aqueous solution such as . This is an improved method for recovering chemicals.
従釆、製紙工場の薬品工程内の薬品バランスを保つため
、ナトリウム循環系等で損失するナトリウム分および回
収ボィラ等で硫化水素、亜硫酸ガス等として損失するィ
オウ分の補給として、ナトリウム分及びィオウ分を、該
薬品回収工程内に補給している。In order to maintain the chemical balance in the chemical process of paper mills, sodium and sulfur components are used to replenish the sodium lost in the sodium circulation system and the sulfur lost as hydrogen sulfide and sulfur dioxide gas in recovery boilers, etc. is supplied into the chemical recovery process.
しかし、本発明の方法を用いることによって、損失ナト
リウム分の補給としてのナトリウム分を、水酸化ナトリ
ウム、炭酸ナトリウムもしくは亜硫酸ナトリウム等のナ
トリウム含有アルカリ水溶液によって行ない、その補給
の過程で、回収ボィラ等の製紙工場薬品回収工程から生
じる、硫化水素、亜硫酸ガス等を含むガスと接触させる
ことによって、それら硫化水素、亜硫酸ガス等を吸収し
、吸収した液は該薬品回収工程に戻すことができ、該薬
品回収工程系外へのィオウ分の損失を抑えるため、損失
ィオウ分補給のためのィオゥ分を、非常に少なくするこ
とができる。ガス中の硫化水素は吸収液に吸収されて、
チオ硫酸ナトリウムまたは、硫酸ナトリウムに変わり、
亜硫酸ガスは亜硫酸ナトリウムまたは硫酸ナトリウムに
変わる。こられの成分は吸収液中の炭酸ナトリウム、酸
性炭酸ナトリウムと共に、抜出し液として薬品回収工程
へ戻される。本発明は亜硫酸バルブ製造の薬品回収工程
等の種々の工程にも適用できるが、次に本発明を組み込
んだクラフトパルプ製造工場における薬品回収工程の一
例を図面によって説明する。However, by using the method of the present invention, the lost sodium is replenished with a sodium-containing alkaline aqueous solution such as sodium hydroxide, sodium carbonate, or sodium sulfite, and in the process of replenishing the sodium, the loss of sodium is replenished. By contacting gas containing hydrogen sulfide, sulfur dioxide gas, etc. generated from the paper mill chemical recovery process, the hydrogen sulfide, sulfur dioxide gas, etc. can be absorbed, and the absorbed liquid can be returned to the chemical recovery process. In order to suppress the loss of sulfur to the outside of the recovery process system, the amount of sulfur for replenishing the lost sulfur can be extremely reduced. Hydrogen sulfide in the gas is absorbed by the absorption liquid,
Converts to sodium thiosulfate or sodium sulfate,
Sulfur dioxide gas turns into sodium sulfite or sodium sulfate. These components, together with sodium carbonate and acidic sodium carbonate in the absorption liquid, are returned to the chemical recovery process as an extraction liquid. Although the present invention can be applied to various processes such as a chemical recovery process in the production of sulfite valves, an example of a chemical recovery process in a kraft pulp manufacturing plant incorporating the present invention will be described below with reference to the drawings.
クラフトパルプ製造の薬品回収工程は、第4図に示す様
に、原料チップ15を蒸鱗工程16でアルカリ性の蒸解
液(白液)80で処理した残溝とパルプを得る。In the chemical recovery process for producing kraft pulp, as shown in FIG. 4, raw material chips 15 are treated with an alkaline cooking liquor (white liquor) 80 in a steaming process 16 to obtain residual grooves and pulp.
蒸解終了後、パルプ及び溶解液をブロータンクヘプロー
した後洗浄工程17へ送り、黒液26とパルプに分離す
る。分離されたパルプは、スクリーン18を経て次の工
程へ送られる。一方黒液26は、濃縮工程19を経て、
薬品として再使用するため、回収ポィラ20では黒液中
の燃擁成分を燃焼させて有機分を除き、有効薬品を分離
回収する。このときソーダ循環系等で損失するソーダ分
および回収ポィラ等で硫化水素、亜硫酸ガスとして損失
するイオウ分補給のために、例えば三硝(Na2SQ)
が補給されなければならない。回収ボィラで得られた溶
融物は、スメルト27と呼ばれ、弱液31に溶解されて
緑液32となる。不溶解残澄を含む粗緑液はクラリフア
イャーでこれらを除いた後、清澄線液は苛性化工程21
へ送られる。苛性化工程21で清澄緑液は生石灰29と
浪合、蝿拝され、苛性化反応を起して緑液中の炭酸ソー
ダが苛性ソーダに変わり白液30となる。白液3川ま清
澄後再び蒸解液として使用する。また、生石灰29は苛
性化工程で苛性化反応により石灰28となるが、これは
白液と分離後、洗浄された後キルン22で焼かれ、生石
灰となり再び塔性化工程で使用される。白液を含む石灰
泥の洗浄後液を弱液31といい、スメルトの溶解に使わ
れる。この様に薬品回収工程は、ほとんどクローズドシ
ステムとなっている。しかし、実際はソーダ循環系等で
のソーダの損失、回収ボィラ等よりの硫化水素、亜硫酸
ガスとして逃げるィオウ分の損失がある。本方法は、こ
の損失ナトリウム分補給に、水酸化ナトリウム、炭酸ナ
トリウムもしくは亜硫酸ナトリウム等の水溶液を用い、
且つその補給の際に、上記補給液を回収ボィラ等よりの
硫化水素、亜硫酸ガスを含むガスに接触させることによ
って、硫化水素、亜硫酸ガス等として薬品回収工程系外
へ逃げる損失ィオウ分を吸収回収し、該薬品回収工程内
の薬品バランスを保つ方法である。After completion of cooking, the pulp and solution are passed through a blow tank and sent to a washing step 17, where they are separated into black liquor 26 and pulp. The separated pulp passes through a screen 18 and is sent to the next process. On the other hand, the black liquor 26 passes through the concentration step 19,
In order to reuse it as a chemical, the recovery polluter 20 burns the combustion components in the black liquor to remove organic components and separate and recover effective chemicals. At this time, in order to replenish the soda content lost in the soda circulation system, etc. and the sulfur content lost as hydrogen sulfide and sulfur dioxide gas in the recovery polluter, for example, trinitrate (Na2SQ) is used.
must be replenished. The melt obtained in the recovery boiler is called smelt 27 and is dissolved in weak liquor 31 to become green liquor 32. After removing the crude green liquor containing undissolved residue with a clarifier, the clarified green liquor is passed through the causticizing step 21.
sent to. In the causticizing step 21, the clarified green liquor is combined with quicklime 29 to cause a causticizing reaction, and the soda carbonate in the green liquor is changed to caustic soda, resulting in a white liquor 30. After the white liquor is clarified, it is used again as a cooking liquor. In addition, the quicklime 29 becomes lime 28 through a causticizing reaction in the causticizing process, and this is separated from the white liquor, washed, and then burned in the kiln 22 to become quicklime and used again in the tower forming process. The washed lime mud containing white liquor is called weak liquor 31 and is used to dissolve smelt. In this way, the chemical recovery process is almost a closed system. However, in reality, there is a loss of soda in the soda circulation system, and a loss of sulfur that escapes as hydrogen sulfide and sulfur dioxide gas from the recovery boiler. This method uses an aqueous solution of sodium hydroxide, sodium carbonate, or sodium sulfite to replenish this lost sodium,
In addition, when replenishing, the replenishment liquid is brought into contact with gas containing hydrogen sulfide and sulfur dioxide gas from a recovery boiler, etc., thereby absorbing and recovering the lost sulfur content that escapes out of the chemical recovery process system as hydrogen sulfide and sulfur dioxide gas. This method maintains the chemical balance in the chemical recovery process.
第4図の二点鎖線内が本発明プロセスである。まず、回
収ボィラ排ガス1をファンによって吸収塔3に導き、吸
収液5をポンプによって吸収塔頂へ送り、気液を向流接
触させ、排ガス中の硫化水素、亜硫酸ガスを吸収液に吸
収する。アルカリ供給として、例えば、炭酸ナトリウム
溶液7を循環タンク4へ供給する。循環タンクは、空気
11で鰻気が行なわれている。触媒は触媒タンクより循
環タンクに供給する。また吸収液の1部は抜出して薬品
回収工程、即ち黒液濃縮工程19、回収ボイラ工程20
、苛性化工程21等へ戻すことができる。ここでは濃縮
工程へ戻した場合を示した。また、戻された液中のチオ
硫酸ソーダ、E硝、亜硫酸ソーダは、薬品回収工程中の
回収ボィラ工程で処理され、硫化ソーダ及び炭酸ソーダ
となるため、系内で蓄積されることはない。以下実施例
について説明する。The process of the present invention is shown within the chain double-dashed line in FIG. First, the recovered boiler exhaust gas 1 is guided to the absorption tower 3 by a fan, and the absorption liquid 5 is sent to the top of the absorption tower by a pump, the gas and liquid are brought into countercurrent contact, and hydrogen sulfide and sulfur dioxide gas in the exhaust gas are absorbed into the absorption liquid. As an alkali supply, for example, a sodium carbonate solution 7 is supplied to the circulation tank 4. In the circulation tank, eel aeration is carried out using air 11. The catalyst is supplied from the catalyst tank to the circulation tank. In addition, a part of the absorption liquid is extracted and used in the chemical recovery process, that is, the black liquor concentration process 19 and the recovery boiler process 20.
, and can be returned to the causticizing step 21 and the like. Here, the case of returning to the concentration step is shown. Furthermore, sodium thiosulfate, E-nitrogen, and sodium sulfite in the returned liquid are treated in the recovery boiler process during the chemical recovery process and become sodium sulfide and soda carbonate, so they are not accumulated in the system. Examples will be described below.
実施例 1
硫化水素、亜硫酸ガスを吸収する際、アルカリ供給液と
して炭酸ナトリウムを用い、吸収液に触媒として、硫酸
第一鉄を添加したアルカリ性水溶液を使用し、且つ吸収
液槽に空気暖気を行った場合の実施例を示す。Example 1 When absorbing hydrogen sulfide and sulfur dioxide gas, sodium carbonate was used as the alkaline supply liquid, an alkaline aqueous solution to which ferrous sulfate was added as a catalyst was used in the absorption liquid, and the absorption liquid tank was heated with air. An example is shown below.
排ガス中の硫化水素、亜硫酸ガスの除去効果は第1図に
示した様に良い結果が得られた。Good results were obtained in removing hydrogen sulfide and sulfur dioxide gas from exhaust gas, as shown in Figure 1.
実施例 2
硫化水素、亜硫酸ガスを吸収する際、アルカリ供V給液
として水酸化ナトリウムを用い、吸収液に触媒として、
硫酸第一鉄及び硫酸マンガンを同時に添加したアルカリ
水溶液を使用し、且つ吸収液槽に空気曝気を行った場合
の実施例を示す。Example 2 When absorbing hydrogen sulfide and sulfur dioxide gas, sodium hydroxide was used as the alkaline supply liquid, and the absorption liquid was used as a catalyst.
An example will be shown in which an alkaline aqueous solution to which ferrous sulfate and manganese sulfate were added at the same time was used, and the absorption liquid tank was aerated with air.
排ガス中の硫化水素、亜硫酸ガスの除去効果は第2図に
示した様に良い結果が得られた。実施例1及び2で用い
た吸収済として充填塔を使用した。Good results were obtained in removing hydrogen sulfide and sulfur dioxide gas from the exhaust gas, as shown in Figure 2. A packed column was used as the absorption column used in Examples 1 and 2.
本実施例1及び2の概略フローシートを第3図に示した
。A schematic flow sheet for Examples 1 and 2 is shown in FIG.
第1図は実施例1の場合の日2SおよびS02除去率を
示し、第2図は実施例2の場合のりSおよびSQ除去率
を示すものであり、第3図は実施例1及びこの概略フロ
−シートを示す。
第4図は、本発明を組み込んだクラフトバルブ製造薬品
回収工程図である。1・・・吸収塔入口ガス、2・・・
吸収塔出口ガス、3・・・吸収塔、4・・・吸収液循環
槽、5・・・吸収液、6・・・抜出し液、7・・・炭酸
ナトリウム水溶液、8・・・水、9・・・炭酸ナトリウ
ム、10…アルカリ溶解槽、11・・・空気、12・・
・ブロア、13・・・触媒、14・・・触媒槽、15・
・・原料チップ、16・・・蒸解工程、17・・・洗蒸
工程、18…スクリーン、16・・・濃縮工程、20・
・・回収ポィラ工程、21・・・苛性化工程、22・・
・キルン、23・・・電気集塵機、24・・・煙突、2
5・・・夫晒しバルブ、26・・・黒液、27・・・ス
メルト、28・・・石灰(CaC03)、29…生石灰
(Ca○)、30・・・白液、31・・・弱液。
第1図第2図
第3図
第4図Figure 1 shows the removal rate of 2S and S02 in Example 1, Figure 2 shows the removal rate of S and SQ in Example 2, and Figure 3 shows the removal rate of Example 1 and its outline. A flow sheet is shown. FIG. 4 is a diagram of a craft valve manufacturing chemical recovery process incorporating the present invention. 1...Absorption tower inlet gas, 2...
Absorption tower outlet gas, 3... Absorption tower, 4... Absorption liquid circulation tank, 5... Absorption liquid, 6... Extraction liquid, 7... Sodium carbonate aqueous solution, 8... Water, 9 ... Sodium carbonate, 10... Alkali dissolution tank, 11... Air, 12...
・Blower, 13... Catalyst, 14... Catalyst tank, 15.
... Raw material chip, 16... Cooking process, 17... Washing and steaming process, 18... Screen, 16... Concentration process, 20.
... Recovery spoiler process, 21... Causticizing process, 22...
・Kiln, 23...Electric dust collector, 24...Chimney, 2
5... Exposed bulb, 26... Black liquor, 27... Smelt, 28... Lime (CaC03), 29... Quicklime (Ca○), 30... White liquor, 31... Weak liquid. Figure 1 Figure 2 Figure 3 Figure 4
Claims (1)
トリウム、炭酸ナトリウム、亜硫酸ナトリウム等のアル
カリ性水溶液を供給して、回収ボイラ工程等製紙工場の
薬品回収工程から生じる排ガスとして逃げる硫化水素、
亜硫酸ガス等を吸収し、該イオン分を回収する方法にお
いて、鉄、マンガンの各塩類を単独に、またはそれらの
混合物を触媒として添加した上記アルカリ性水溶液を吸
収液として、pH8.3〜pH10.0の範囲で用い、
硫化水素、亜硫酸ガス等を吸収した後の液は、そのまま
当該薬品回収工程に戻すことを特徴とする製紙工場にお
ける薬品回収の改良方法。1. In the chemical recovery process at a paper mill, alkaline aqueous solutions such as sodium hydroxide, sodium carbonate, and sodium sulfite are supplied, and hydrogen sulfide escapes as exhaust gas generated from the paper mill's chemical recovery process, such as the recovery boiler process.
In the method of absorbing sulfur dioxide gas etc. and recovering the ion content, the above alkaline aqueous solution to which iron and manganese salts alone or a mixture thereof are added as a catalyst is used as an absorption liquid, and the pH is 8.3 to 10.0. Used within the range of
An improved method for recovering chemicals in a paper mill, characterized in that the liquid after absorbing hydrogen sulfide, sulfur dioxide gas, etc. is returned as is to the chemical recovery process.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51122913A JPS6015758B2 (en) | 1976-10-15 | 1976-10-15 | Improved methods for chemical recovery in paper mills |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51122913A JPS6015758B2 (en) | 1976-10-15 | 1976-10-15 | Improved methods for chemical recovery in paper mills |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5349105A JPS5349105A (en) | 1978-05-04 |
| JPS6015758B2 true JPS6015758B2 (en) | 1985-04-22 |
Family
ID=14847697
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51122913A Expired JPS6015758B2 (en) | 1976-10-15 | 1976-10-15 | Improved methods for chemical recovery in paper mills |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6015758B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP6396582B2 (en) * | 2014-05-08 | 2018-09-26 | ヒンドゥスタン ペトロリアム コーポレーション リミテッド | Removal of sulfide in waste caustic stream over active solid phase catalyst |
-
1976
- 1976-10-15 JP JP51122913A patent/JPS6015758B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5349105A (en) | 1978-05-04 |
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