JPS5825520B2 - Method for removing carbon dioxide gas from gas generated by methane fermentation method - Google Patents
Method for removing carbon dioxide gas from gas generated by methane fermentation methodInfo
- Publication number
- JPS5825520B2 JPS5825520B2 JP55020403A JP2040380A JPS5825520B2 JP S5825520 B2 JPS5825520 B2 JP S5825520B2 JP 55020403 A JP55020403 A JP 55020403A JP 2040380 A JP2040380 A JP 2040380A JP S5825520 B2 JPS5825520 B2 JP S5825520B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- carbon dioxide
- liquid
- line
- tank
- 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
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Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/40—Capture or disposal of greenhouse gases of CO2
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Gas Separation By Absorption (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Description
【発明の詳細な説明】
本発明は、メタン発酵法で発生したガス中の炭酸ガスを
除去する方法に関し、特に建設コストおよび運転コスト
の極めて低い上記方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing carbon dioxide from gas generated in a methane fermentation method, and particularly to the above-mentioned method with extremely low construction and operating costs.
従来、メタン発酵法で生成されたガス中の炭酸ガスは第
1図A、Bに示す方法で除去されていた。Conventionally, carbon dioxide gas in gas produced by methane fermentation has been removed by the methods shown in FIGS. 1A and 1B.
第1図Aにおいては、メタン発酵槽I内のメタン菌と原
料有機物との混合液状物1から発生したガス2がライン
3を経て浮屋根式ガスタンク■に導入される。In FIG. 1A, gas 2 generated from a liquid mixture 1 of methane bacteria and raw organic matter in a methane fermentation tank I is introduced into a floating roof type gas tank 2 through a line 3.
該ガスタンク■における5はガス6の留り具合に応じて
上下する浮屋根、7は水等の液体である。In the gas tank (2), numeral 5 is a floating roof that moves up and down depending on how much gas 6 remains therein, and 7 is a liquid such as water.
該ガスタンク■内のガス6は利用状況に応じてライン8
から抜出され、脱酸塔■へ導かれる。Gas 6 in the gas tank ■ is transferred to line 8 depending on usage conditions.
It is extracted from the tank and led to the deoxidizing tower (■).
該脱酸塔■ではライン9から補給さKる清水やアルカリ
等の脱酸剤(後述するライン17から排出される液を再
生回収し、高価なアミン類を添加したものが多用される
)10が、ポンプ13、ライン15、散布ノズル16を
経て循環されており、該脱酸剤10が散布ノズル16か
ら充填材11内を流下する際に上記のガスと気液接触し
、該ガス中の炭酸ガスを吸収する。In the deoxidizing tower (2), a deoxidizing agent such as fresh water or alkali is supplied from line 9 (recycled liquid discharged from line 17, which will be described later, is often used, and expensive amines are added thereto) 10 is circulated through the pump 13, line 15, and spray nozzle 16, and when the deoxidizer 10 flows down from the spray nozzle 16 into the filler 11, it comes into gas-liquid contact with the above gas, and the Absorbs carbon dioxide gas.
この炭酸ガスを吸収した液は、脱酸剤10の水位を制御
する機器類12からの電気信号によって作動するバルブ
(電動弁、電磁弁等)あるいはポンプ14によって、脱
酸剤の効力を失わぬようライン9から補給される量に見
合って、ライン1Tから排出される。The liquid that has absorbed this carbon dioxide gas is processed by a valve (electric valve, solenoid valve, etc.) or pump 14 that is operated by an electric signal from equipment 12 that controls the water level of the deoxidizer 10 to prevent it from losing its deoxidizing effect. The amount is discharged from line 1T in proportion to the amount replenished from line 9.
一方、炭酸ガスが除去されメタン濃度の上昇したガスは
ライン18からガス利用系へ送られる。On the other hand, the gas from which carbon dioxide has been removed and whose methane concentration has increased is sent from line 18 to the gas utilization system.
勿論、ライン8からライン18へ至るラインが充填材1
1を一回通過するだけで充分な効果を示さない場合は、
ライン18内のガスを一部あるいは大部分、ライン8の
ムロへプロワ等で戻し、充填材11を何回か通過させる
ようにしてもよい。Of course, the line from line 8 to line 18 is filler material 1.
If passing 1 once does not show sufficient effect,
Part or most of the gas in the line 18 may be returned to the drain in the line 8 using a blower or the like, and the gas may be passed through the filler 11 several times.
第1図Bは、ガスタンク■′として圧力容器式のものを
用いた場合で、脱酸塔■における炭酸ガス除去態様は上
記の第1図Aと同じである。FIG. 1B shows a case where a pressure vessel type gas tank (2) is used, and the manner in which carbon dioxide is removed in the deoxidizing column (2) is the same as in FIG. 1A above.
なお、第1図Bにおける4はコンプレッサ、22は電磁
弁あるいは電動弁、22は減圧弁、19 、20 。In addition, in FIG. 1B, 4 is a compressor, 22 is a solenoid valve or an electric valve, 22 is a pressure reducing valve, 19, 20.
21は圧力を制御する機器類でコンプレッサ4や電磁(
動)弁22に稼動停止の信号を与えるものである。21 is equipment for controlling pressure, such as compressor 4 and electromagnetic (
This is to give a signal to the valve 22 to stop its operation.
しかし、第1図A、Bに示す方法には次のような欠点が
ある。However, the methods shown in FIGS. 1A and 1B have the following drawbacks.
(1)脱酸塔■本体が可燃性ガスを扱うため、シールや
躯体にメタン発酵槽I、ガスタンクn 、 n’と同様
の高価な構造を必要とし、建設コストが高くつくばかり
でなく、運転にも注意を要する。(1) Deoxidizing tower■ Because the main body handles flammable gas, it requires an expensive structure similar to the methane fermentation tank I and gas tanks n and n' for seals and frames, which not only increases construction costs but also reduces operational costs. Also requires caution.
(2)ライン9から脱酸剤を定常的に注入する必要があ
り、運転コストが大きい。(2) It is necessary to constantly inject the deoxidizing agent from the line 9, resulting in high operating costs.
(3)第1図Bに示す方法では圧力制御機器類19゜2
0.21や電磁(動)弁22や減圧弁22のような複雑
な制御系が必要であり、しかも可燃ガスの制御系は非常
に機器ブレイドが高いばかりでなく、運転も複雑となる
。(3) In the method shown in Figure 1B, pressure control equipment 19°2
A complicated control system such as 0.21, electromagnetic (operated) valve 22, and pressure reducing valve 22 is required, and the control system for combustible gas not only requires a very high number of equipment, but also has complicated operation.
(4)メタン発酵槽Iで発生したガスは40〜50係も
の炭酸ガスを含み、これから炭酸ガスを除去するシステ
ムにおいて、一旦ガスタンク■。(4) The gas generated in the methane fermentation tank I contains 40 to 50 carbon dioxide gas, and in the system to remove carbon dioxide gas from it, it is first transferred to the gas tank ■.
■′に貯留すること自体、ガスタンクn 、 n’が莫
大となり、無駄である。Storing the gas in ■' itself requires an enormous amount of gas tanks n and n', which is wasteful.
本発明は、
(1)炭酸ガスの除去に際して、アルカリ特にアミン等
の特別の薬剤を使用せず、清水の新規な補給も殆んど必
要とせず、(省資源、低運転コスト)
(11)可燃ガスの取扱いラインを簡単にし、(危険回
避、コスト低減)
(iii) ガスタンクを小さくすると共に、脱酸塔
を安いコストで製作できるようにする
ことを目的とするものである。The present invention has the following features: (1) When removing carbon dioxide gas, no special chemicals such as alkalis or amines are used, and almost no new supply of fresh water is required (resource saving and low operating costs) (11) The purpose is to simplify the handling line for combustible gas (avoid danger, reduce costs), (iii) to reduce the size of the gas tank, and to manufacture the deoxidizing tower at low cost.
上記目的は、メタン発酵法で発生したガスをガスタンク
内で水と接触させて該ガス中の炭酸ガスを吸収除去し、
該炭酸ガス吸収液をガスタンク外へ取出し、大気と接触
させて該液中の炭酸ガスを大気側へ放出させ、該炭酸ガ
ス放出液を再び前記ガスタンク内へ循環させることを特
徴とする前記ガス中の炭酸ガス除去方法によって達成す
ることができる。The above purpose is to bring the gas generated by methane fermentation into contact with water in a gas tank to absorb and remove carbon dioxide from the gas,
The carbon dioxide absorbing liquid is taken out of the gas tank, brought into contact with the atmosphere to release the carbon dioxide in the liquid to the atmosphere, and the carbon dioxide releasing liquid is circulated back into the gas tank. This can be achieved by the carbon dioxide removal method.
以下、添付図面に沿って本発明方法を詳細に説明する。Hereinafter, the method of the present invention will be explained in detail with reference to the accompanying drawings.
第2図は本発明方法の一実施態様を示す説明図である。FIG. 2 is an explanatory diagram showing one embodiment of the method of the present invention.
第2図において、■はメタン発酵槽、1はメタン発酵し
ている液体で、原料有機物にメタン菌群が作用し、次の
反応によりガス2が発生する。In FIG. 2, ■ is a methane fermentation tank, 1 is a liquid undergoing methane fermentation, a group of methane bacteria acts on the raw organic material, and gas 2 is generated by the next reaction.
原料有機物+(場合によってはH20)
→CH4↑+CO2↑+(場合によってはH20)なお
、CH4とCO2の比はCH4が50〜60係、C02
が 50〜40%である。Raw material organic matter + (in some cases H20) → CH4↑+CO2↑+ (in some cases H20) The ratio of CH4 to CO2 is CH4 is 50-60%, C02
is 50-40%.
上記のガス2はライン3から浮屋根式ガスタンク■1に
導入される。The above gas 2 is introduced from line 3 into floating roof type gas tank 1.
該ガスタンク■1の5は浮屋根、6はガス、7は清水に
類似する仕様の水、28は後述するライン27から供給
される液(水)の散布ノズル、29は気液接触用の充填
材である。5 of the gas tank 1 is a floating roof, 6 is gas, 7 is water with specifications similar to fresh water, 28 is a spray nozzle for liquid (water) supplied from line 27, which will be described later, and 29 is a filling for gas-liquid contact. It is a material.
このガスタンク■1において、ガス6はライン27から
の液(水)と気液接触し、次の反応が起る。In this gas tank (1), the gas 6 comes into gas-liquid contact with the liquid (water) from the line 27, and the following reaction occurs.
■ CO2+H20=H++HCO3−ヰ2H”+C0
−−・・・・・・・・・・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・・・・・・・(1)
■ CO2のままで水に溶解する。■ CO2+H20=H++HCO3−ヰ2H”+C0
−−・・・・・・・・・・・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・・・・・・・・・(1)
■ Dissolves in water as CO2.
・・・・・・・・・・・・・・・・・・(2)ところで
ライン3から送られて来るガスはCO2が上記したよう
に50〜40係と大量であるため、大量のCO2が溶解
し、■の反応は当然■印の方へ移行し、一部はHCO3
−として、またCO3−一として多量に溶解する。・・・・・・・・・・・・・・・・・・(2) By the way, the gas sent from line 3 contains a large amount of CO2, ranging from 50 to 40, as mentioned above, so it contains a large amount of CO2. is dissolved, and the reaction of ■ naturally shifts to the one marked with ■, and some of it is HCO3.
It dissolves in large quantities as - and as CO3-.
この液はポンプ26によりガスタンク■1から抜出され
、一部または大部分が上記のライン27から該ガスタン
ク■1内へ循環供給される。This liquid is drawn out from the gas tank (1) by the pump 26, and part or most of it is circulated and supplied into the gas tank (1) through the above-mentioned line 27.
一方、CO□が除去されたガスはライン18から利用系
へ送られる。On the other hand, the gas from which CO□ has been removed is sent from line 18 to the utilization system.
なお、ライン18内のガスは、CH480〜90係、残
りは主にCO2で10〜20%である。The gas in the line 18 is CH480-90, and the rest is mainly CO2 at 10-20%.
また上記の液はライン30から脱酸塔■1へ導入され、
底部の液留31へ貯留される。In addition, the above liquid is introduced from line 30 to deoxidizing tower ■1,
It is stored in the liquid reservoir 31 at the bottom.
該液留31内の液はポンプ32で抜出され、ライン33
を経て上記のガスタンク馬内の仕様水7として循環使用
され、またライン34から脱酸塔■、へ循環さ札スプレ
ィノズル35から気液接触用の充填材11へ散布される
。The liquid in the liquid reservoir 31 is extracted by a pump 32 and sent to a line 33.
The water is circulated and used as the specified water 7 in the gas tank, and is also circulated from the line 34 to the deoxidizing tower (2) and sprayed from the spray nozzle 35 to the gas-liquid contact filler 11.
この脱酸塔■1においては、ファン36によって外気を
ライン38から導入し、ライン37から放出しているが
、この外気が充填材11を通過する際に上記の液と接触
し、次の反応が起り、該液中のCO2,HCO3−2C
O3−一が外気中へ除去される。In this deoxidizing tower (1), outside air is introduced through line 38 by fan 36 and released through line 37. When this outside air passes through packing material 11, it comes into contact with the above liquid and is used for the next reaction. occurs, and CO2, HCO3-2C in the liquid
O3-1 is removed to the outside air.
2H++C03−=H++HC03−jC02↑+HO
・・・・・・・・・・・・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・・・・・・・・・・
・(3)すなわち、大気中の002は一般に0.03%
程度なので、反応は当然矢印の方へ移行し、CO2のま
まで溶解していたものも含めて、CO2として外気中へ
放出され、液は脱酸されるのである。2H++C03-=H++HC03-jC02↑+HO
・・・・・・・・・・・・・・・・・・・・・・・・
・・・・・・・・・・・・・・・・・・・・・・・・
・(3) In other words, 002 in the atmosphere is generally 0.03%
Therefore, the reaction naturally moves in the direction of the arrow, and even the dissolved CO2 is released into the outside air as CO2, and the liquid is deoxidized.
なお、図中の12は液留31の水位を制御する機器類で
、電気信号によって上記したポンプ26を作動させるも
のである。Note that 12 in the figure is equipment for controlling the water level of the liquid distillate 31, and operates the above-mentioned pump 26 by an electric signal.
以上のように、メタン発酵槽■で発生したガス中に含ま
れているCO2は、浮屋根式ガスタンク■1内で、該タ
ンク■、のシール用に使用されている液7によって吸収
され、この液に吸収されたCO□が脱酸塔■1内におい
て、大気外へ放出され、一方CO2を放出した液は再び
上記のガスタンク■1へ戻り、上記ガス中のCO2の吸
収用液として使用されるのである。As mentioned above, the CO2 contained in the gas generated in the methane fermentation tank (2) is absorbed in the floating roof gas tank (1) by the liquid 7 used for sealing the tank (2). The CO□ absorbed in the liquid is released to the outside of the atmosphere in the deoxidizing tower ■1, while the liquid that has released CO2 returns to the gas tank ■1 and is used as a liquid for absorbing the CO2 in the gas. It is.
液は系内を循環するが、ガスはタンク■、に止どまった
ままで、やがてライン18から利用系へ送られる。The liquid circulates within the system, but the gas remains in the tank (2) and is eventually sent to the utilization system through the line 18.
ライン18内のガスは、C04度が一般に10〜20係
に低下しているが、これを更に低下させるには、充填材
29あるいはポンプ26からライン33へ至る系の設計
や仕様を変えて大きい能力をもたらすようにしたり、あ
るいはガスタンク用1内の貯留時間を長くすればよい。The C04 degree of the gas in the line 18 has generally decreased to 10 to 20 degrees, but in order to further reduce this, the design and specifications of the system from the filler 29 or pump 26 to the line 33 must be changed. The storage time in the gas tank 1 may be increased.
この貯留時間が長い程CO2は減じる。The longer this storage time, the less CO2 is produced.
なお、常温の清水にCO□が溶解する量は、1気圧下で
ほぼ同容積であり、一方同じガスに含まれるCH4の水
への溶解量はたかだか0.05容量であり、本発明方法
で失われるメタンは微々たるものである。Note that the amount of CO□ dissolved in fresh water at room temperature is approximately the same volume under 1 atm, while the amount of CH4 contained in the same gas dissolved in water is at most 0.05 volume. The amount of methane lost is negligible.
また、本発明におけるCO2の除去は、ガスタンク用1
内の7の水量と6の最大容積が同じ場合、6でのガス滞
留時間の、7と脱酸浴用との液移動時間に対する割合が
同等以上で成立つものであり、その液移動時間中にガス
タンク■1および脱酸基■1が充分機能を発揮すればよ
く、第2図に示す態様および後述の第3図の態様のもの
は余裕をもって成立っている。In addition, the removal of CO2 in the present invention is performed using 1 for gas tank.
If the water volume in 7 and the maximum volume in 6 are the same, the ratio of the gas residence time in 6 to the liquid transfer time for 7 and the deoxidizing bath is equal or greater, and during that liquid transfer time, the gas tank It is only necessary that (1) and the deoxidizing group (1) fully exhibit their functions, and the embodiment shown in FIG. 2 and the embodiment shown in FIG. 3, which will be described later, are well established.
第3図は本発明方法の他の実施態様を示すもので、CO
#去作用は上記した第2図の場合と同じであるが、次の
点で第2図の場合と異なる。FIG. 3 shows another embodiment of the method of the present invention, in which CO
#The action is the same as in the case of Fig. 2 described above, but differs from the case of Fig. 2 in the following points.
第3図においては、ガスタンク■2内のガス6をライン
23、ポンプ24、ガスディフューザ25を循環させて
液7と充分接触させ、上記1,2の反応によりCO2を
液7へ吸収除去する。In FIG. 3, the gas 6 in the gas tank 2 is circulated through the line 23, the pump 24, and the gas diffuser 25 to bring it into sufficient contact with the liquid 7, and CO2 is absorbed and removed by the liquid 7 through the reactions 1 and 2 above.
このCO2を吸収した液はライン39、ポンプ40を経
て脱酸基(これは水槽である)I2へ導入する。The liquid that has absorbed this CO2 is introduced into the deoxidizing group (this is a water tank) I2 via a line 39 and a pump 40.
導入された液41は、コンプレッサまたはプロワ43で
ライン44から導きディフューザ45から放出される外
気と接触し、この接触を充分に行なうための充填材11
を通過中に、上記3の反応等によりCO2が液から外気
側へ移行し、外気と共にライン46から大気中へ放出さ
れる。The introduced liquid 41 is brought into contact with the outside air guided from a line 44 by a compressor or blower 43 and discharged from a diffuser 45, and the filler 11 is used to sufficiently effect this contact.
While passing through the liquid, CO2 moves from the liquid to the outside air side due to the reaction described in 3 above, and is released into the atmosphere from the line 46 along with the outside air.
このようにしてC02が除去された液は、ライン42か
らガスタンク■2へ循環使用される。The liquid from which C02 has been removed in this way is circulated through the line 42 to the gas tank (2).
なお、第3図において、ライン18から利用系へ送るガ
スのCO2濃度を10〜20%以下に減じさせるには、
第2図の場合と同様ガスタンク用2内のガスの貯留時間
を長くするか、あるいはディフューザ25やポンプ24
の設計や仕様を変えて大きい能力をもたすようにすれば
よい。In addition, in FIG. 3, in order to reduce the CO2 concentration of the gas sent from the line 18 to the utilization system to 10 to 20% or less,
As in the case of Fig. 2, either increase the storage time of the gas in the gas tank 2, or
The design and specifications of the system can be changed to provide greater capacity.
以上説明した本発明方法の効果をまとめると次の通りで
ある。The effects of the method of the present invention explained above are summarized as follows.
(a) 従来の脱酸基は可燃ガス取扱い装置であった
ため、密閉度が要求され、かつ使用電気機器が防爆基準
のものでなければならなかったのに対し、本発明の脱酸
基は水を処理対象とするので雑な作り方でよく、大幅に
コストダウンとなる。(a) Conventional deoxidizing groups were used for combustible gas handling equipment, which required airtightness and the electrical equipment used had to meet explosion-proof standards; however, the deoxidizing group of the present invention Since the target is processed, it does not need to be made in a sloppy manner, resulting in a significant cost reduction.
(b) 従来のガスタンクは除去すべきCO2の貯留
をも行なっており、該C02がメタン発酵発生ガスの半
分近くを占めているため、容量の大きいものであったが
、本発明のガスタンクは、該タンク内でCO□をどんど
ん吸収除去するため、容量は従来のものの約4でよく、
大幅なコストダウンとなる。(b) Conventional gas tanks also store CO2 to be removed, and this CO2 accounts for nearly half of the gas generated by methane fermentation, so they have a large capacity, but the gas tank of the present invention has a large capacity. Since CO□ is rapidly absorbed and removed within the tank, the capacity is only about 4 liters compared to conventional tanks.
This results in a significant cost reduction.
(c) コストの高い電気制御系がない。(c) There is no expensive electrical control system.
(d)従来の脱酸基で必要としていた脱酸剤または多量
の新規清水が一切不要である。(d) There is no need for a deoxidizing agent or a large amount of fresh water, which were required with conventional deoxidizing groups.
(e) 可燃ガスの取扱い系はガスタンクまでであり
、極めてシンプルである。(e) The combustible gas handling system is extremely simple, with only a gas tank.
Cf)“以上のような効果を発揮しつつ、メタン発酵で
得られるガスのカロリーを約2倍程度上昇させることが
できる。Cf) “It is possible to increase the calories of gas obtained by methane fermentation by about twice while exhibiting the above effects.
第1図A、Bは従来のメタン発酵法で発生したガス中の
炭酸ガス除去法を示す説明図 第2,3図は本発明方法
による該ガス中の炭酸ガス除去法の一実施態様例を示す
説明図である。FIGS. 1A and 1B are explanatory diagrams showing a method for removing carbon dioxide gas from gas generated by the conventional methane fermentation method. FIGS. FIG.
Claims (1)
接触させて該ガス中の炭酸ガスを吸収除去し、該炭酸ガ
ス吸収液をガスタンク外へ取出し、大気と接触させて該
液中の炭酸ガスを大気側へ放出させ、該炭酸ガス放出液
を再び前記ガスタンク内へ循環させることを特徴とする
前記ガス中の炭酸ガス除去方法。1. Gas generated by methane fermentation is brought into contact with water in a gas tank to absorb and remove carbon dioxide from the gas, and the carbon dioxide absorption liquid is taken out of the gas tank and brought into contact with the atmosphere to remove carbon dioxide from the liquid. A method for removing carbon dioxide from the gas, characterized in that the carbon dioxide gas is released into the atmosphere, and the carbon dioxide releasing liquid is circulated back into the gas tank.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55020403A JPS5825520B2 (en) | 1980-02-22 | 1980-02-22 | Method for removing carbon dioxide gas from gas generated by methane fermentation method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55020403A JPS5825520B2 (en) | 1980-02-22 | 1980-02-22 | Method for removing carbon dioxide gas from gas generated by methane fermentation method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS56118791A JPS56118791A (en) | 1981-09-17 |
| JPS5825520B2 true JPS5825520B2 (en) | 1983-05-27 |
Family
ID=12026052
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP55020403A Expired JPS5825520B2 (en) | 1980-02-22 | 1980-02-22 | Method for removing carbon dioxide gas from gas generated by methane fermentation method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5825520B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4990255B2 (en) * | 2008-10-09 | 2012-08-01 | 株式会社神鋼環境ソリューション | Algae culture apparatus and algae culture method |
| JP5392598B2 (en) * | 2008-10-29 | 2014-01-22 | 地方独立行政法人大阪府立産業技術総合研究所 | Gas purification equipment |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS576988B2 (en) * | 1974-04-24 | 1982-02-08 | ||
| JPS5930478B2 (en) * | 1976-12-06 | 1984-07-27 | 株式会社日立製作所 | Anaerobic digestion method for organic waste liquid |
-
1980
- 1980-02-22 JP JP55020403A patent/JPS5825520B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS56118791A (en) | 1981-09-17 |
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