JPS5836625B2 - Regeneration method of inorganic adsorbent - Google Patents
Regeneration method of inorganic adsorbentInfo
- Publication number
- JPS5836625B2 JPS5836625B2 JP50014328A JP1432875A JPS5836625B2 JP S5836625 B2 JPS5836625 B2 JP S5836625B2 JP 50014328 A JP50014328 A JP 50014328A JP 1432875 A JP1432875 A JP 1432875A JP S5836625 B2 JPS5836625 B2 JP S5836625B2
- Authority
- JP
- Japan
- Prior art keywords
- regeneration
- activated carbon
- liquid ammonia
- ammonia
- inorganic adsorbent
- 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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- Water Treatment By Sorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【発明の詳細な説明】
本発明は無機吸着剤の再生、特に液体アンモニアを用い
た無機吸着剤の再生法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to the regeneration of inorganic adsorbents, and in particular to a method for regenerating inorganic adsorbents using liquid ammonia.
活性炭に代表される無機吸着剤(以下活性炭を例にとり
説明する)のひん度は近年増加の一途をたどり、例えば
高次水処理における活性炭吸着法或いは悪臭に関して溶
媒等を活性炭で回収すること等にも利用されており、今
や使用済活性炭を再生することは資源的見地からもます
ます重要になってきている。The use of inorganic adsorbents such as activated carbon (described below using activated carbon as an example) has been increasing in popularity in recent years. Activated carbon is also being used, and recycling spent activated carbon is now becoming increasingly important from a resource standpoint.
従来より活性炭の再生は熱再生法や湿式法など種々の方
法が考えられているが、現在、湿式法では完全な方法が
見いだされていない。Conventionally, various methods have been considered for regenerating activated carbon, such as a thermal regeneration method and a wet method, but a perfect wet method has not yet been found.
これは活性炭に吸着されるすべての有機物を脱着せしめ
る流体が見い出されないためであった。This was because no fluid was found that could desorb all the organic matter adsorbed on activated carbon.
たとえば、フェノールを吸着せしめた活性炭は苛性ソー
ダ溶液で洗浄しフエノラートにして溶解させて再生を、
また塩の溶液を使用して電解酸化を行ない活性炭を再生
する方法など種々知られている。For example, activated carbon that has adsorbed phenol can be regenerated by washing it with a caustic soda solution and dissolving it into phenolate.
Various methods are also known, including a method for regenerating activated carbon by electrolytic oxidation using a salt solution.
しかし、これらを含む湿式法では被吸着物質が限定され
、都市下水の処理に使用した活性炭など種々雑多な有機
物が吸着している活性炭の再生は不可能に近い。However, in wet methods including these, the substances to be adsorbed are limited, and it is almost impossible to regenerate activated carbon, which has adsorbed various organic substances, such as activated carbon used for treating municipal sewage.
このことが活性炭の湿式再生法の第1の欠点であり汎用
性を欠くところである。This is the first drawback of the wet regeneration method of activated carbon, and it lacks versatility.
また脱着に使用した流体の処理が必要であることも欠点
の一つであり、湿式法は特定の目的に使用した活性炭に
しか適用されないのが現状である。Another disadvantage is that the fluid used for desorption must be treated, and the wet method is currently only applicable to activated carbon used for a specific purpose.
又、熱再生法は、加熱炉内に活性炭を入れ、活性炭に吸
着した物質を炭化させ、その後加熱炉内に供給された酸
化性ガス(水蒸気あるいは空気)と炭化物を縮合させ活
性炭を再生するものであり活性炭自身の燃焼によるロス
、表面積の低下等により再生後の吸着能力が著しく減少
するのが常である。In addition, the thermal regeneration method is a method in which activated carbon is placed in a heating furnace, the substances adsorbed on the activated carbon are carbonized, and then the oxidizing gas (steam or air) supplied into the heating furnace is condensed with the carbide to regenerate the activated carbon. Therefore, the adsorption capacity after regeneration usually decreases significantly due to loss due to combustion of activated carbon itself, decrease in surface area, etc.
本発明の目的は、上記した従来技術の欠点をなくし、都
市下水の処理に使用した活性炭等をも再生できる新規な
無機吸着剤の再生法を提供するにある。An object of the present invention is to provide a novel method for regenerating an inorganic adsorbent, which eliminates the drawbacks of the prior art described above and can also regenerate activated carbon used in the treatment of municipal sewage.
本発明は係る点に鑑み、常温、常圧では気体であるアン
モニアを、液体の状態で無機吸着剤に接触せしめ、被吸
着物質を液体アンモニアに溶解させて再生を行なうもの
である。In view of this, the present invention regenerates ammonia, which is a gas at room temperature and pressure, by bringing it into contact with an inorganic adsorbent in a liquid state, and dissolving the adsorbed substance in the liquid ammonia.
即ち、本発明になる再生法は、液体アンモニアが非常に
よ《有機物を溶解せしめ、がつ塩の化合物をも溶解させ
る溶媒であるため、無機吸着剤の形状、吸着能力など物
理的および化学的性質を伺も変えることなく再生するこ
とが可能である。In other words, in the regeneration method of the present invention, liquid ammonia is a solvent that dissolves organic substances very well and also dissolves salt compounds. It is possible to reproduce it without changing its properties.
また、従来の湿式法では常温、常圧において液体を使用
するものであり、再生に使用した液体の後処理が問題と
なるが、本発明の液体アンモニアを使用する再生では圧
を常圧に解放することによりガス化し、被吸着物質と容
易に分離することができる。In addition, in the conventional wet method, liquid is used at room temperature and pressure, and post-treatment of the liquid used for regeneration becomes a problem, but in the regeneration using liquid ammonia of the present invention, the pressure is released to normal pressure. By doing so, it can be gasified and easily separated from the adsorbed substance.
液体アンモニアで洗浄された無機吸着剤には若干のアン
モニアが残りアンモニア臭がするが、水洗を行なえば除
去できる。Although some ammonia remains on the inorganic adsorbent washed with liquid ammonia and gives off an ammonia odor, it can be removed by washing with water.
以下本発明の一実施例を添付図面に基づいて説明する。An embodiment of the present invention will be described below based on the accompanying drawings.
第1図において、液体アンモニア貯蔵タンク1内の液体
アンモニアは高圧送液ポンプ8で再生塔7に送られ、圧
力調節弁6で液体状態に保たれる。In FIG. 1, liquid ammonia in a liquid ammonia storage tank 1 is sent to a regeneration tower 7 by a high-pressure liquid sending pump 8, and maintained in a liquid state by a pressure regulating valve 6.
この場合温度(常温)25℃では飽和蒸気圧は10kg
/crAであるので、約15kg/crAの圧に保つよ
うにすれば再生塔γ内は十分にアンモニアを液体にする
ことができる。In this case, at a temperature (normal temperature) of 25°C, the saturated vapor pressure is 10 kg.
/crA, so if the pressure is maintained at about 15 kg/crA, ammonia can be sufficiently liquefied in the regeneration tower γ.
再生塔T内で液体アンモニアと活性炭は接触し、被吸着
物質は液体アンモニアに溶解あるいは反応して脱着され
る。Liquid ammonia and activated carbon come into contact within the regeneration tower T, and the adsorbed substance is dissolved or reacted with the liquid ammonia and desorbed.
被吸着物質を含む液体アンモニアは圧力調節弁6を出た
あと常圧に解放され、ガス分離器5でアンモニアと脱着
有機物が分離される。After the liquid ammonia containing the adsorbed substance exits the pressure control valve 6, it is released to normal pressure, and the ammonia and the desorbed organic substance are separated in the gas separator 5.
ガス状のアンモニアはコンプレッサー4で液化され脱水
塔2(例えばアルミナ充てん塔)で水分を除去され、液
体アンモニア貯蔵タンク1に帰還される。Gaseous ammonia is liquefied by a compressor 4, moisture is removed by a dehydration tower 2 (for example, an alumina-packed tower), and then returned to the liquid ammonia storage tank 1.
ここで液体アンモニアの圧縮膨張に伴なう熱は送風ファ
ン3で放冷あるいは放熱され、温度は均一化される。Here, the heat accompanying the compression and expansion of liquid ammonia is cooled or radiated by the blower fan 3, and the temperature is made uniform.
再生操作を行なったあと、停止弁12.14を閉じ停止
弁13を開き、三方切換弁16をコンプレッサー側にし
てコンプレッサーで再生塔内の液体アンモニアを取り除
く。After performing the regeneration operation, the stop valves 12 and 14 are closed, the stop valve 13 is opened, and the three-way switching valve 16 is set to the compressor side to remove liquid ammonia in the regeneration tower with the compressor.
そのあと停止弁13を閉じ、三方切換弁15,16,1
7を水洗の流路になるように保つ。After that, the stop valve 13 is closed, and the three-way switching valves 15, 16, 1
Keep 7 so that it becomes a water flow path.
水洗ポンプ10で水を再生塔7に送り、微量残存するア
ンモニアガスを水に溶解させ洗浄水タンク9に導く。Water is sent to the regeneration tower 7 by the water washing pump 10, and a trace amount of remaining ammonia gas is dissolved in the water, and the water is introduced to the washing water tank 9.
水に溶解したアンモニアはH型の陽イオン交換樹脂塔1
1で除去される。Ammonia dissolved in water is H-type cation exchange resin tower 1
1 is removed.
この陽イオン交換樹脂がアンモニアで飽和された場合、
硫酸水で洗浄することにより再生される。When this cation exchange resin is saturated with ammonia,
Regenerated by washing with sulfuric acid water.
ほとんどの有機化合物は水よりもはるかに液体アンモニ
アによく溶け、炭化水素類をはじめ、アルコール、カル
ボン酸、エステル、アルデヒド、ケトン、エーテル、ア
ルキル硫酸、アミン、アミド、ヘテロ環化合物などその
溶解度は非常に大きい。Most organic compounds are much more soluble in liquid ammonia than in water; hydrocarbons, alcohols, carboxylic acids, esters, aldehydes, ketones, ethers, alkyl sulfates, amines, amides, heterocyclic compounds, etc. have very high solubility. big.
また塩(NH4Ciなと)や金属(アルカリ金属など)
を溶解させる溶媒でもあることが知られており、活性炭
等の無機吸着剤の再生に使用する溶媒として非常に優れ
ていることを見いだした。Also, salts (NH4Ci) and metals (alkali metals, etc.)
It is also known that it is a solvent that dissolves carbon, and it has been found that it is an excellent solvent for use in the regeneration of inorganic adsorbents such as activated carbon.
実施例 1
活性汚泥法では除去されないABS等の洗剤の一つであ
るドデシルベンゼンスルホン酸ソーダ(以下DBS と
記す)を被吸着物質として本法による再生を検討した。Example 1 Regeneration by this method was investigated using sodium dodecylbenzenesulfonate (hereinafter referred to as DBS), which is one of the detergents such as ABS that cannot be removed by the activated sludge method, as an adsorbed substance.
球形の活性炭1グのDBS2 6 0 ppmでの平衡
吸着量は、48■DBS/P活性炭であり、この活性炭
を乾燥した後、再生塔に51入れ、液体アンモニアを1
.2ml/minの流量で流した。The equilibrium adsorption amount of 1 g of spherical activated carbon at 60 ppm of DBS2 is 48 ■ DBS/P activated carbon. After drying this activated carbon, 51 g of activated carbon is placed in a regeneration tower, and 1 g of liquid ammonia is added to the activated carbon.
.. The flow rate was 2 ml/min.
この時の室温は21℃で、圧力調節弁で圧力を20kg
/crtiに保った。At this time, the room temperature was 21℃, and the pressure was adjusted to 20kg using the pressure control valve.
/crti was maintained.
第2図に液体アンモニアの流通時間(液体アンモニア量
)と再生率の関係を示した。Figure 2 shows the relationship between the distribution time of liquid ammonia (the amount of liquid ammonia) and the regeneration rate.
ここで再生率は、液体アンモニアで洗浄したあとの活性
炭のDBS平衡吸着量と当初新品で求めた平衡吸着量(
吸着等温線から)との割合から求めた。Here, the regeneration rate is the equilibrium adsorption amount of DBS of the activated carbon after washing with liquid ammonia and the equilibrium adsorption amount (
(from the adsorption isotherm).
図から明らかなように、流通時間15分、液体アンモニ
ア量18ml(約122)で55%の再生率を示し、活
性炭重量の4.8倍量(液体アンモニア量36rrLA
!,24f)でほぼ85%の再生率が得られた。As is clear from the figure, the regeneration rate was 55% with a flow time of 15 minutes and a liquid ammonia amount of 18 ml (approx.
! , 24f), a regeneration rate of approximately 85% was obtained.
更に液体アンモニア量を増し108rrLl(36グ)
で再生率は92%が得られた。Further increase the amount of liquid ammonia to 108rrLl (36g)
A regeneration rate of 92% was obtained.
これ以上の量では再生率はあまり向上しなかった。If the amount was higher than this, the reproduction rate did not improve much.
100%の再生率が得られなかったのは、活性炭の微細
孔に入り吸着したものの脱着が非常に困難であると考え
られる。The reason why a 100% regeneration rate could not be obtained is considered to be that it is extremely difficult to desorb the adsorbed substances that entered the micropores of the activated carbon.
しかし、再生率は80〜90%が達成されれば、十分に
目的が達成されたものといってよい。However, if a regeneration rate of 80 to 90% is achieved, it can be said that the objective has been fully achieved.
DBS はおそらくアンモニウム塩になって液体アンモ
ニアに溶解したと考えられる。DBS probably became an ammonium salt and dissolved in liquid ammonia.
十数回の実験後、ガス分離器50入口管の内面近傍およ
び、分離器内表面上に白い粉末状のものが一面に薄《附
着していた。After more than ten experiments, a thin layer of white powder was observed near the inner surface of the inlet pipe of the gas separator 50 and on the inner surface of the separator.
実施例 2
アミンおよびカルボン酸類の化合物の代表としてアミノ
酸のフエニルアラニンを被吸着物質として、本法による
再生を検討した。Example 2 Regeneration by this method was investigated using the amino acid phenylalanine as a representative of amine and carboxylic acid compounds as an adsorbed substance.
実施例1と同様球形活性炭を使用し、フエニルアラニン
110ppmでの平衡吸着量は120■/1活性炭で、
この吸着済み活性炭の51を再生塔に入れ、実施例10
条件で再生を行なった。As in Example 1, spherical activated carbon was used, and the equilibrium adsorption amount at 110 ppm of phenylalanine was 120 μ/1 activated carbon.
Example 10 51 of this adsorbed activated carbon was put into a regeneration tower.
Playback was performed under these conditions.
第3図に液体アンモニアの流通時間(液体アンモニア量
)と再生率の関係を示した。Figure 3 shows the relationship between the distribution time of liquid ammonia (the amount of liquid ammonia) and the regeneration rate.
液体アンモニ7量1 8rrLl( 1 2P)で再生
率は78%が得られ、先のDBS よりもフエニルア
ラニンは液体アンモニアに非常によく溶解することがわ
かる。A regeneration rate of 78% was obtained with 7 amounts of liquid ammonia (18rrLl (12P)), indicating that phenylalanine dissolves much better in liquid ammonia than in the previous DBS.
活性炭重量の4.8倍量で、ほぼ90%の再生が可能で
あることがわかった。It was found that approximately 90% regeneration was possible with an amount 4.8 times the weight of activated carbon.
この場合もやはりフエニルアラニンのカルボキシル基が
アンモニウム塩の形になり液体アンモニアに溶解するも
のと考えられる。In this case as well, it is thought that the carboxyl group of phenylalanine becomes an ammonium salt and dissolves in liquid ammonia.
実施例 3
フェノールを被吸着物質として本法による再生を行なっ
た。Example 3 Regeneration was carried out using this method using phenol as the adsorbed substance.
活性炭は実施例1と同様に球形活性炭を使用したが、フ
ェノール2 0 0 ppmでの平衡吸着量は160■
/1活性炭で、実施例1と同様の条件で再生を行なった
。Spherical activated carbon was used as in Example 1, but the equilibrium adsorption amount at 200 ppm of phenol was 160.
Regeneration was carried out under the same conditions as in Example 1 using /1 activated carbon.
第4図に液体アンモニアの流通時間(液体アンモニア量
)と再生率の関係を示した。FIG. 4 shows the relationship between the distribution time of liquid ammonia (the amount of liquid ammonia) and the regeneration rate.
図から明らかなようにフェノールは先のフエニルアラニ
ンよりも液体アンモニアによく溶けることがわかる。As is clear from the figure, phenol is more soluble in liquid ammonia than phenylalanine.
すなわち液体アンモニア量18rrLlで再生率は82
%が得られ、これは活性炭重量の2.4倍であり、少な
い量の液体アンモニアで再生が可能であることを示す。In other words, the regeneration rate is 82 with a liquid ammonia amount of 18rrLl.
%, which is 2.4 times the weight of activated carbon, indicating that regeneration is possible with small amounts of liquid ammonia.
また液体アンモニア量108l71l(82グ)でほぼ
100%に近い再生率が得られた。Furthermore, a regeneration rate close to 100% was obtained with an amount of liquid ammonia of 108 liters and 71 liters (82 grams).
この結果からアルコール類や水酸基をもつベンゼンなど
の活性炭からの脱着、すなわち再生に非常に有効な溶媒
であることがわかる。This result shows that it is a very effective solvent for the desorption, or regeneration, of alcohols and benzene with hydroxyl groups from activated carbon.
比較例 I
DBS を吸着せしめた活性炭(49■/グ活性炭)の
51を再生塔に入れ、再生塔温度110℃、再生塔内圧
力60ky/c4に保ち流量1.75TILl/Tni
!L(ポンプの指示)で1時間かけて再生を行なった。Comparative Example I Activated carbon (49μ/g activated carbon) 51 which had adsorbed DBS was placed in a regeneration tower, and the regeneration tower temperature was maintained at 110°C and the regeneration tower internal pressure was maintained at 60ky/c4 and the flow rate was 1.75TILl/Tni.
! Regeneration was performed at L (pump instruction) for 1 hour.
再生率は22%で、再生は本条件で困難であった。The regeneration rate was 22%, and regeneration was difficult under these conditions.
ちなみにこの再生条件ではアンモニアは高密度のガス状
態である。By the way, under these regeneration conditions, ammonia is in a high-density gas state.
比較例 2
DBS を吸着せしめた活性炭(4877I!l;I/
1活性炭)の51を再生塔に入れ再生塔温度140℃、
再生塔圧力1 2 0 kg/crAに保ち、流量1.
75ml/minで1時間かげて再生した。Comparative Example 2 Activated carbon adsorbed with DBS (4877I!l; I/
1 activated carbon) into the regeneration tower, the regeneration tower temperature was 140℃,
The regeneration tower pressure was maintained at 120 kg/crA, and the flow rate was 1.
It was regenerated at 75 ml/min for 1 hour.
再生したあとの活性炭のDBS吸着量は20.21n9
/P活性炭であり、再生率は42%であった。The DBS adsorption amount of activated carbon after regeneration is 20.21n9
/P activated carbon, and the regeneration rate was 42%.
この再生条件ではアンモニアは超臨界状態であり、高密
度のガスを使用したときよりも再生率は良かったが、実
施例1の液体で使用したときの再生率の半分以下であっ
た。Under these regeneration conditions, ammonia was in a supercritical state, and the regeneration rate was better than when a high-density gas was used, but it was less than half the regeneration rate when the liquid of Example 1 was used.
以上のように、本発明はアンモニアを液体の状態で使用
することにより、種々の有機物を吸着した活性炭に代表
される無機吸着剤の再生が可能である。As described above, in the present invention, by using ammonia in a liquid state, it is possible to regenerate inorganic adsorbents such as activated carbon that have adsorbed various organic substances.
第1図は本発明を実施する為の系統図、第2図、第3図
および第4図はそれぞれ被吸着物質が違う場合における
液体アンモニア流通時間(液体アンモニア量)と再生率
の関係を示す図である。
1・・・・・・液体アンモニア貯蔵タンク、2・・・・
・・脱水塔、4・・・・・・コンプレッサー、5・・・
・・・ガス分離器、6・・・・・・圧力調節弁、7・・
・・・・再生塔、8・・・・・・高圧送液ポンプ、9・
・・・・・洗浄水タンク、10・・・・・・水洗ポンプ
、11・・・・・・陽イオン交換樹脂塔。Figure 1 is a system diagram for carrying out the present invention, and Figures 2, 3, and 4 show the relationship between liquid ammonia flow time (liquid ammonia amount) and regeneration rate for different adsorbed substances, respectively. It is a diagram. 1...Liquid ammonia storage tank, 2...
...Dehydration tower, 4...Compressor, 5...
...Gas separator, 6...Pressure control valve, 7...
... Regeneration tower, 8 ... High pressure liquid pump, 9.
. . . Washing water tank, 10 . . . Washing pump, 11 . . . Cation exchange resin tower.
Claims (1)
いて、洗浄剤として液体アンモニア(超臨界流体を除く
)を用いたことを特徴とする無機吸着剤の再生法。 2 無機吸着剤を洗浄することにより再生する方法にお
いて、無機吸着剤を液体アンモニア(超臨界流体を除く
)により洗浄し、しかる後水洗することを特徴とする無
機吸着剤の再生法。 3 無機吸着剤を洗浄することにより再生する方法にお
いて、無機吸着剤を液体アンモニア(超臨界流体を除く
)で洗浄することにより被吸着物質を液体アンモニアに
溶解せしめ、しかる後液体アンモニアをガス化すること
により被吸着物を分離することを特徴とする無機吸着剤
の再生法。[Scope of Claims] 1. A method for regenerating an inorganic adsorbent by washing it, characterized in that liquid ammonia (excluding supercritical fluid) is used as a cleaning agent. 2. A method for regenerating an inorganic adsorbent by washing it, which comprises washing the inorganic adsorbent with liquid ammonia (excluding supercritical fluid) and then washing it with water. 3 In a method of regenerating an inorganic adsorbent by washing it, the inorganic adsorbent is washed with liquid ammonia (excluding supercritical fluid) to dissolve the adsorbed substance in liquid ammonia, and then the liquid ammonia is gasified. A method for regenerating an inorganic adsorbent, which is characterized by separating adsorbed substances.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50014328A JPS5836625B2 (en) | 1975-02-05 | 1975-02-05 | Regeneration method of inorganic adsorbent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50014328A JPS5836625B2 (en) | 1975-02-05 | 1975-02-05 | Regeneration method of inorganic adsorbent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5189888A JPS5189888A (en) | 1976-08-06 |
| JPS5836625B2 true JPS5836625B2 (en) | 1983-08-10 |
Family
ID=11857990
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP50014328A Expired JPS5836625B2 (en) | 1975-02-05 | 1975-02-05 | Regeneration method of inorganic adsorbent |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5836625B2 (en) |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5853939U (en) * | 1981-10-07 | 1983-04-12 | 株式会社昭和製作所 | Hydraulic shock absorber gas filling device |
| US5899552A (en) * | 1993-11-11 | 1999-05-04 | Enplas Corporation | Surface light source device |
| JPH07169311A (en) | 1993-12-17 | 1995-07-04 | Enplas Corp | Light scattering light guide light source device and liquid crystal display device |
| US5982540A (en) * | 1994-03-16 | 1999-11-09 | Enplas Corporation | Surface light source device with polarization function |
| US7119047B1 (en) | 2001-02-26 | 2006-10-10 | C And T Company, Inc. | Modified activated carbon for capacitor electrodes and method of fabrication thereof |
| JP2017121631A (en) * | 2017-04-17 | 2017-07-13 | 株式会社日立製作所 | Adsorbent regenerator |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4124528A (en) * | 1974-10-04 | 1978-11-07 | Arthur D. Little, Inc. | Process for regenerating adsorbents with supercritical fluids |
-
1975
- 1975-02-05 JP JP50014328A patent/JPS5836625B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5189888A (en) | 1976-08-06 |
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