JPH11344200A - Reserving method for digestion gas - Google Patents
Reserving method for digestion gasInfo
- Publication number
- JPH11344200A JPH11344200A JP15085498A JP15085498A JPH11344200A JP H11344200 A JPH11344200 A JP H11344200A JP 15085498 A JP15085498 A JP 15085498A JP 15085498 A JP15085498 A JP 15085498A JP H11344200 A JPH11344200 A JP H11344200A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- methane
- adsorbed
- adsorbing material
- filled
- 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.)
- Granted
Links
Landscapes
- Filling Or Discharging Of Gas Storage Vessels (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、下水処理場、ビー
ル製造工場、家畜・家禽類(牛、豚、鶏など)の飼育場で
の廃棄物処理場などにおける生物学的処理に際し発生す
る消化ガスの貯蔵方法に関し、より詳細には、消化ガス
中のメタンガスを効率的に回収/貯蔵し、得られたメタ
ンを燃料として有効利用する方法に関する。The present invention relates to digestion generated during biological treatment in a sewage treatment plant, a beer manufacturing plant, a waste treatment plant in a livestock and poultry (cattle, pig, chicken, etc.) breeding plant. More particularly, the present invention relates to a method for efficiently collecting / storing methane gas in digestive gas and effectively using the obtained methane as fuel.
【0002】[0002]
【従来の技術】従来からも、上述の生物学的処理を大規
模に行う処理施設(以下「大規模処理施設」ということ
がある)では、発生ガスを常圧あるいは加圧下にガスホ
ルダーに貯蔵し、必要に応じて発電用あるいは加熱用の
原料として使用することが、行われている。しかしなが
ら、従来の貯蔵方法においては、貯蔵密度が低いので、
大規模なガスホルダーが必要となり、そのための十分な
設置スペースが得られない場合には、発生ガスの一部を
そのまま燃焼放散させている。また、小規模処理施設で
は、発生ガスの殆どを有効に利用することなく、そのま
ま燃焼放散している。2. Description of the Related Art Conventionally, in a treatment facility for performing the above-mentioned biological treatment on a large scale (hereinafter sometimes referred to as a "large-scale treatment facility"), generated gas is stored in a gas holder under normal pressure or under pressure. It is used as a power generation or heating raw material as needed. However, in the conventional storage method, since the storage density is low,
If a large-scale gas holder is required and sufficient installation space cannot be obtained, a part of the generated gas is burned and diffused as it is. Further, in a small-scale treatment facility, most of the generated gas is burned and emitted without being used effectively.
【0003】[0003]
【発明が解決しようとする課題】従って、本発明は、処
理設備の規模の大小にかかわりなく、生物学的処理に伴
って発生する消化ガスを全量有効利用する技術を提供す
ることを主な目的とする。SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide a technique for effectively utilizing the entire amount of digestive gas generated during a biological treatment regardless of the size of a treatment facility. And
【0004】[0004]
【課題を解決するための手段】本発明者は、上記の様な
技術の現状に留意しつつ、研究を重ねた結果、吸着材を
使用する場合には、消化ガスを効率よく貯蔵することが
可能となり、生物学的処理設備の規模に関係なく、消化
ガス中の有用成分をほぼ全量利用し得ることを見出し
た。すなわち、本発明は、下記の消化ガスの貯蔵方法を
提供するものである: 1.生物学的処理に際し発生する消化ガスをそのままあ
るいは各ガス成分に分離した後、吸着貯蔵することを特
徴とする消化ガスの貯蔵方法。 2.吸着貯蔵するガスが、メタン、二酸化炭素および硫
化水素である上記項1に記載の方法。 3.吸着貯蔵するガスが、メタンである請求項1に記載
の方法。 4.吸着材が、活性炭、ゼオライト、シリカゲルおよび
有機錯体金属の少なくとも1種である上記項1に記載の
方法。 5.消化ガス中の各成分を硫化水素、二酸化炭素および
メタンの順序で分離し、メタンを吸着貯蔵する上記項1
に記載の方法。Means for Solving the Problems The inventors of the present invention have studied repeatedly while paying attention to the current state of the technology as described above. As a result, when an adsorbent is used, the digestion gas can be stored efficiently. It has been found that almost all the useful components in the digestive gas can be used regardless of the size of the biological treatment equipment. That is, the present invention provides the following digestion gas storage method: A method for storing a digestive gas, wherein the digestive gas generated during biological treatment is adsorbed and stored as it is or after being separated into individual gas components. 2. Item 2. The method according to Item 1, wherein the gas to be stored by adsorption is methane, carbon dioxide and hydrogen sulfide. 3. The method according to claim 1, wherein the gas to be absorbed and stored is methane. 4. Item 2. The method according to Item 1, wherein the adsorbent is at least one of activated carbon, zeolite, silica gel and an organic complex metal. 5. Item 1 in which the components in the digested gas are separated in the order of hydrogen sulfide, carbon dioxide and methane, and methane is absorbed and stored.
The method described in.
【0005】[0005]
【発明の実施の形態】本発明においては、(A)消化ガス
中の硫化水素、二酸化炭素およびメタンをこの順序で分
離した後、メタンを吸着材を充填したタンク内に吸着貯
蔵するか、あるいは(B)消化ガス中の硫化水素と二酸化
炭素とを同時に除去した後、メタンを吸着材を充填した
タンク内に吸着貯蔵するか、(C)消化ガスの主成分であ
るメタン、二酸化炭素および硫化水素を混合状態で、吸
着材を充填したタンク内に吸着貯蔵する。本発明におい
ては、消化ガス中の主成分を相互に分離し、高純度のメ
タンを吸着貯蔵する(A)法がより好ましい。以下におい
ては、主に(A)法について、詳細に説明する。BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, (A) hydrogen sulfide, carbon dioxide and methane in a digested gas are separated in this order, and then methane is adsorbed and stored in a tank filled with an adsorbent, or (B) After simultaneously removing hydrogen sulfide and carbon dioxide in digested gas, methane is adsorbed and stored in a tank filled with an adsorbent, or (C) methane, carbon dioxide and sulfide, which are main components of digested gas, Hydrogen is adsorbed and stored in a mixed state in a tank filled with an adsorbent. In the present invention, the method (A) of separating the main components in the digested gas from each other and adsorbing and storing high-purity methane is more preferable. Hereinafter, the method (A) will be mainly described in detail.
【0006】(A)法においては、まず、消化ガスを脱硫
用の吸着材が充填されている吸着塔に通し、硫化水素を
吸着・除去する。吸着材としては、従来から脱硫剤とし
て使用されている活性炭、ゼオライト、金属酸化物(酸
化銅、酸化亜鉛など)が例示される。吸着時の温度およ
び圧力は、消化ガス発生状態そのままでも良く、特に制
限されないが、温度は、通常常温〜100℃程度(より好ま
しくは、常温〜60℃程度)であり、圧力は、常圧〜1MPa
程度である。脱硫操作は、バッチ方式で行っても良く、
或いは2塔以上を使用して、脱硫操作と脱硫剤の再生操
作とを交互に行う連続再生処理方式で行っても良い。脱
硫用吸着材の再生は、吸着塔に加熱水蒸気を吹き込ん
で、硫化水素を分離することにより行われる。In the method (A), first, the digestion gas is passed through an adsorption tower filled with an adsorbent for desulfurization to adsorb and remove hydrogen sulfide. Examples of the adsorbent include activated carbon, zeolite, and metal oxides (copper oxide, zinc oxide, etc.) conventionally used as desulfurizing agents. The temperature and pressure at the time of adsorption may be the digestion gas generation state as it is and are not particularly limited, but the temperature is usually from normal temperature to about 100 ° C (more preferably, from normal temperature to about 60 ° C), and the pressure is from normal pressure to 1MPa
It is about. The desulfurization operation may be performed in a batch mode,
Alternatively, the continuous desulfurization operation and the desulfurization agent regeneration operation may be alternately performed using two or more columns to perform a continuous regeneration treatment. The regeneration of the desulfurization adsorbent is performed by blowing heated steam into the adsorption tower to separate hydrogen sulfide.
【0007】硫化水素を吸着・除去された消化ガスは、
次いで、二酸化炭素吸着材が充填された吸着塔に通され
る。この吸着材としては、従来から二酸化炭素の吸着材
として使用されている活性炭、ゼオライト、有機金属錯
体(フマル酸銅、シクロヘキサンジカルボン酸銅、スチ
ルベンジカルボン酸銅、テレフタル酸銅、ターフェニル
ジカルボン酸、ビフェニルジカルボン酸銅、トランジカ
ルボン酸銅など)などが例示される。吸着時の温度およ
び圧力は、特に制限されないが、温度は常温〜100℃程
度(より好ましくは、常温或いはその近傍)であり、圧力
は常圧〜1MPa程度(より好ましくは、常圧或いはその近
傍)である。二酸化炭素の吸着操作も、バッチ方式で行
っても良く、或いは2塔以上を使用してPSA方式で行って
も良い。PSA方式によれば、純度99%以上の高純度メタ
ンを得ることができる。また、二酸化炭素吸着材の再生
も、脱硫用吸着材の再生と同様にして行うことができ
る。The digestion gas from which hydrogen sulfide has been adsorbed and removed is
Then, it is passed through an adsorption tower filled with a carbon dioxide adsorbent. Examples of the adsorbent include activated carbon, zeolite, and organic metal complexes (copper fumarate, copper cyclohexanedicarboxylate, copper stilbene dicarboxylate, copper terephthalate, terphenyldicarboxylic acid, biphenyl) conventionally used as carbon dioxide adsorbents. Copper dicarboxylate, copper transdicarboxylate, etc.). The temperature and pressure during adsorption are not particularly limited, but the temperature is about room temperature to about 100 ° C. (more preferably, room temperature or near room temperature), and the pressure is about room pressure to about 1 MPa (more preferably, room temperature or about room temperature). ). The operation of adsorbing carbon dioxide may be performed by a batch method or by a PSA method using two or more columns. According to the PSA method, high-purity methane with a purity of 99% or more can be obtained. The regeneration of the carbon dioxide adsorbent can be performed in the same manner as the regeneration of the desulfurization adsorbent.
【0008】かくして得られたメタンを貯蔵タンク内に
充填された吸着材に吸着させ、貯蔵する。吸着時の温度
および圧力は、特に制限されないが、温度は通常常温〜
100℃程度(より好ましくは、常温或いはその近傍)であ
り、圧力は、常圧〜3.4MPa程度である。メタン吸着材と
しては、活性炭、ゼオライト、シリカゲル、有機金属錯
体(フマル酸銅、シクロヘキサンジカルボン酸銅、スチ
ルベンジカルボン酸銅、テレフタル酸銅、ターフェニル
ジカルボン酸、ビフェニルジカルボン酸銅、トランジカ
ルボン酸銅など)などが例示される。これらのメタン吸
着材は、単独で或いは2種以上を併用することができ
る。メタン吸着材として活性炭、ゼオライト或いはシリ
カゲルを使用する場合には、比表面積はできるだけ大き
いことが好ましく、実用上少なくとも1000m2/g以上であ
ることを必要とする。また、その細孔径は通常4〜12Å
程度であり、より好ましくは8〜12Å程度である。[0008] The methane thus obtained is adsorbed on an adsorbent filled in a storage tank and stored. The temperature and pressure during adsorption are not particularly limited, but the temperature is usually from room temperature to normal temperature.
The temperature is about 100 ° C. (more preferably, at or near room temperature), and the pressure is from about normal pressure to about 3.4 MPa. As the methane adsorbent, activated carbon, zeolite, silica gel, organic metal complexes (copper fumarate, copper cyclohexanedicarboxylate, copper stilbene dicarboxylate, copper terephthalate, terphenyldicarboxylic acid, copper biphenyldicarboxylate, copper transdicarboxylate, etc.) And the like. These methane adsorbents can be used alone or in combination of two or more. When activated carbon, zeolite or silica gel is used as the methane adsorbent, the specific surface area is preferably as large as possible and practically required to be at least 1000 m 2 / g or more. Also, its pore size is usually 4 ~ 12mm
Degree, more preferably about 8 to 12 degrees.
【0009】メタン吸着時の温度および圧力は、メタン
収得時そのままの温度および圧力でも良く、特に制限さ
れないが、温度は、通常常温〜100℃程度(より好ましく
は、常温〜60℃程度)であり、圧力は、常圧以上(より好
ましくは常圧〜3.4MPa程度)である。貯蔵圧力を高める
必要がある場合には、コンプレッサーによりメタンを昇
圧した後、吸着し、貯蔵する。The temperature and pressure at the time of methane adsorption may be the same as the temperature and pressure at the time of obtaining methane, and are not particularly limited. The temperature is usually about normal temperature to 100 ° C. (more preferably about normal temperature to 60 ° C.). The pressure is equal to or higher than normal pressure (more preferably, normal pressure to about 3.4 MPa). When it is necessary to increase the storage pressure, methane is pressurized by a compressor, then adsorbed and stored.
【0010】(B)法においては、消化ガスを吸収液とし
ての水酸化ナトリウム水溶液(好ましくは20〜40%程度)
中にバブリングすることにより、消化ガスの硫化水素と
二酸化炭素とを同時に分離除去した後、(A)法と同様に
して、メタン(純度93%以上)を吸着材を充填したタンク
内に吸着貯蔵する。[0010] In the method (B), an aqueous solution of sodium hydroxide (preferably about 20 to 40%) is used as an absorption liquid for digestion gas.
Hydrogen sulfide and carbon dioxide in the digested gas are simultaneously separated and removed by bubbling inside, and methane (purity 93% or more) is adsorbed and stored in a tank filled with adsorbent in the same manner as in method (A). I do.
【0011】[0011]
【発明の効果】本発明によれば、吸着材を充填したガス
ホルダーを使用して、消化ガス或いは消化ガスから分離
回収したメタンを貯蔵することにより、ガスホルダーを
小型化し、貯蔵施設の設備コストを低減させることがで
きる。According to the present invention, a gas holder filled with an adsorbent is used to store digestive gas or methane separated and recovered from digestive gas, thereby reducing the size of the gas holder and reducing the equipment cost of a storage facility. Can be reduced.
【0012】従って、本発明によれば、処理設備の規模
の大小にかかわりなく、生物学的処理に伴って発生する
消化ガスを有効利用することが可能となる。Therefore, according to the present invention, it is possible to effectively use the digestion gas generated during the biological treatment regardless of the size of the treatment equipment.
【0013】[0013]
【実施例】以下に実施例を示し、本発明の特徴とすると
ころをより一層明確にする。 実施例1 下水処理場において発生した消化ガス4000Nm3をゼオラ
イト充填塔を通過させて硫化水素を吸着除去し、次いで
活性炭充填塔を通過させて二酸化炭素を吸着除去した。EXAMPLES Examples are shown below to further clarify the features of the present invention. Example 1 4000 Nm 3 of digested gas generated in a sewage treatment plant was passed through a zeolite packed tower to adsorb and remove hydrogen sulfide, and then passed through an activated carbon packed tower to adsorb and remove carbon dioxide.
【0014】かくして得られた99%メタン2600Nm3は、
粉末活性炭(比表面積1400m2/g)78トンを充填した124m3
のガスホルダーに常温且つ常圧で貯蔵することが可能で
あった。 比較例1 実施例1と同様の消化ガス4000Nm3を従来法に従って常
温且つ常圧で貯蔵するためには、4000m3のガスホルダー
が必要であった。 実施例2 実施例1と同様にして得た99%メタン2600Nm3を実施例
1と同様の粉末活性炭を使用して、常温かつ1.0MPaの圧
力で吸着したところ、26トンの粉末活性炭を充填する37
m3のガスホルダーにより貯蔵を行うことが可能であっ
た。 比較例2 実施例1と同様の消化ガス4000Nm3を常温且つ1.0MPaの
圧力で吸着貯蔵するためには、400m3のガスホルダーが
必要であった。 実施例3 実施例1と同様にして得た99%メタン2600Nm3を実施例
1と同様の粉末活性炭を使用して、常温かつ3.4MPaの圧
力で吸着したところ、18トンの粉末活性炭を充填する23
m3のガスホルダーにより貯蔵を行うことが可能であっ
た。 比較例3 実施例1と同様の消化ガス4000Nm3を常温且つ3.4MPaの
圧力で吸着貯蔵するためには、114m3のガスホルダーが
必要であった。The thus obtained 99% methane (2600Nm 3)
124 m 3 filled with 78 tons of powdered activated carbon (specific surface area 1400 m 2 / g)
At normal temperature and normal pressure. Comparative Example 1 In order to store 4000 Nm 3 of the digested gas as in Example 1 at normal temperature and normal pressure according to the conventional method, a gas holder of 4000 m 3 was required. 99% methane 2600 nm 3 obtained in the same manner as in Example 1 using the same powdered activated carbon as in Example 1, was adsorbed at a pressure of normal temperature and 1.0 MPa, to fill 26 tons of powdered activated carbon 37
Storage was possible with an m 3 gas holder. Comparative Example 2 In order to adsorb and store 4000 Nm 3 of the same digestive gas as in Example 1 at normal temperature and a pressure of 1.0 MPa, a 400 m 3 gas holder was required. Example 3 99% methane (2600 Nm 3) obtained in the same manner as in Example 1 was adsorbed at room temperature and a pressure of 3.4 MPa using the same powdered activated carbon as in Example 1, and filled with 18 tons of powdered activated carbon. twenty three
Storage was possible with an m 3 gas holder. Comparative Example 3 In order to adsorb and store 4000 Nm 3 of the same digestive gas as in Example 1 at normal temperature and a pressure of 3.4 MPa, a gas holder of 114 m 3 was required.
Claims (5)
のままあるいは各ガス成分に分離した後、吸着貯蔵する
ことを特徴とする消化ガスの貯蔵方法。1. A method for storing a digestive gas, wherein a digestive gas generated during a biological treatment is adsorbed and stored as it is or after being separated into respective gas components.
および硫化水素である請求項1に記載の方法。2. The method according to claim 1, wherein the gas to be adsorbed and stored is methane, carbon dioxide and hydrogen sulfide.
1に記載の方法。3. The method according to claim 1, wherein the gas to be adsorbed and stored is methane.
ルおよび有機錯体金属の少なくとも1種である請求項1
に記載の方法。4. The method according to claim 1, wherein the adsorbent is at least one of activated carbon, zeolite, silica gel and an organic complex metal.
The method described in.
素およびメタンの順序で分離し、メタンを吸着貯蔵する
請求項1に記載の方法。5. The method according to claim 1, wherein the components in the digested gas are separated in the order of hydrogen sulfide, carbon dioxide and methane, and the methane is adsorbed and stored.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP15085498A JP3870276B2 (en) | 1998-06-01 | 1998-06-01 | Methane storage method and methane purification and storage facility |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP15085498A JP3870276B2 (en) | 1998-06-01 | 1998-06-01 | Methane storage method and methane purification and storage facility |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH11344200A true JPH11344200A (en) | 1999-12-14 |
JP3870276B2 JP3870276B2 (en) | 2007-01-17 |
Family
ID=15505831
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP15085498A Expired - Lifetime JP3870276B2 (en) | 1998-06-01 | 1998-06-01 | Methane storage method and methane purification and storage facility |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3870276B2 (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2000053971A1 (en) * | 1999-03-05 | 2000-09-14 | Toyota Jidosha Kabushiki Kaisha | Method for storing natural gas by adsorption and adsorbing agent for use therein |
JP2001187998A (en) * | 1999-12-28 | 2001-07-10 | Osaka Gas Co Ltd | Digestive gas adsorptive storage device |
JP2002327897A (en) * | 2001-05-01 | 2002-11-15 | Osaka Gas Co Ltd | Natural gas adsorbing and storing device and method |
JP2003035399A (en) * | 2000-08-11 | 2003-02-07 | Osaka Gas Co Ltd | Adsorbing and storing device and adsorbing and storing method for natural gas |
US6613126B2 (en) | 1998-09-30 | 2003-09-02 | Toyota Jidosha Kabushiki Kaisha | Method for storing natural gas by adsorption and adsorbing agent for use therein |
JP2009249571A (en) * | 2008-04-09 | 2009-10-29 | Taiyo Nippon Sanso Corp | Method for eliminating hydrogen sulfide contained in biogas |
JP2018525453A (en) * | 2015-06-01 | 2018-09-06 | カルゴン カーボン コーポレーション | Method for inactivating activated carbon in a biogas refiner |
-
1998
- 1998-06-01 JP JP15085498A patent/JP3870276B2/en not_active Expired - Lifetime
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6613126B2 (en) | 1998-09-30 | 2003-09-02 | Toyota Jidosha Kabushiki Kaisha | Method for storing natural gas by adsorption and adsorbing agent for use therein |
WO2000053971A1 (en) * | 1999-03-05 | 2000-09-14 | Toyota Jidosha Kabushiki Kaisha | Method for storing natural gas by adsorption and adsorbing agent for use therein |
JP2001187998A (en) * | 1999-12-28 | 2001-07-10 | Osaka Gas Co Ltd | Digestive gas adsorptive storage device |
JP2003035399A (en) * | 2000-08-11 | 2003-02-07 | Osaka Gas Co Ltd | Adsorbing and storing device and adsorbing and storing method for natural gas |
JP2002327897A (en) * | 2001-05-01 | 2002-11-15 | Osaka Gas Co Ltd | Natural gas adsorbing and storing device and method |
JP2009249571A (en) * | 2008-04-09 | 2009-10-29 | Taiyo Nippon Sanso Corp | Method for eliminating hydrogen sulfide contained in biogas |
JP2018525453A (en) * | 2015-06-01 | 2018-09-06 | カルゴン カーボン コーポレーション | Method for inactivating activated carbon in a biogas refiner |
JP2021073333A (en) * | 2015-06-01 | 2021-05-13 | カルゴン カーボン コーポレーション | Method for inerting activated carbon in biogas purification machine |
Also Published As
Publication number | Publication date |
---|---|
JP3870276B2 (en) | 2007-01-17 |
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