JPH11114552A - Method for recovering valuable materials from organic waste liquid - Google Patents

Method for recovering valuable materials from organic waste liquid

Info

Publication number
JPH11114552A
JPH11114552A JP9286857A JP28685797A JPH11114552A JP H11114552 A JPH11114552 A JP H11114552A JP 9286857 A JP9286857 A JP 9286857A JP 28685797 A JP28685797 A JP 28685797A JP H11114552 A JPH11114552 A JP H11114552A
Authority
JP
Japan
Prior art keywords
ammonia
organic
org
waste liquid
inorg
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.)
Pending
Application number
JP9286857A
Other languages
Japanese (ja)
Inventor
Takashi Kawamura
高 川村
Shigeki Horii
重希 堀井
Nobuhiro Oda
信博 織田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP9286857A priority Critical patent/JPH11114552A/en
Publication of JPH11114552A publication Critical patent/JPH11114552A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To effectively separate and recover valuable materials from an org. waste liq. by adding an alkali to the waste liq., gasifying ammonia by aeration, adding an org. solvent to the liq. freed from ammonia to extract inorg. salts and heating the liq. from which the inorg. salts are removed to volatilize off and separate the org. solvent. SOLUTION: The org. waste liq. is admixed with an alkali in a mixing tank 1 and brought into countercurrent contact with air in a stripping tower 2, and the ammonia ion in the org. waste liq. is separated as gaseous ammonia. The gaseous ammonia obtained is reacted with an aq. inorg. acid soln. in an absorption tower 3 and recovered in a storage tank 4 as an aq. soln. of inorg. acid ammonium. Meanwhile, to the effluent of the stripping tower 2 an org. solvent is added in a salting-out tank 5, the inorg. salt is separated and removed by the salting-out effect, and the inorg. salt is dehydrated by a centrifugal separator 6 and then charged into a storage tank 7. The supernatant water of the salting- out tank 5 is preheated by a heat exchanger 8 and then heated by a vaporizer 9, the org. solvent is volatilized off, and the concd. org. matter soln. is stored in a storage tank 10.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は食品発酵廃液等の有
機性廃液からの有価物の回収方法に係り、特にアンモニ
アイオン、無機酸イオン及び有機物を含有する有機性廃
液を処理するに当り、廃液中のアンモニア、無機塩及び
有機物を効率的に分離回収する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for recovering valuable resources from organic waste liquids such as food fermentation waste liquids, and more particularly, to treating organic waste liquids containing ammonia ions, inorganic acid ions and organic substances. The present invention relates to a method for efficiently separating and recovering ammonia, inorganic salts, and organic substances in water.

【0002】[0002]

【従来の技術】従来、有機性廃液は、一般に、廃液を希
釈して、メタン発酵、活性汚泥処理などのいわゆる水処
理技術を用いて処理するか、或いは、濃厚廃液をそのま
ま燃焼させることにより処理されている。
2. Description of the Related Art Conventionally, organic waste liquid is generally treated by diluting the waste liquid and using a so-called water treatment technique such as methane fermentation or activated sludge treatment, or by burning a concentrated waste liquid as it is. Have been.

【0003】このような有機性廃液の処理法では、燃焼
による熱利用が行われているのみで、廃液中の成分を分
離回収して有効利用を図ることはできなかった。
In such a method of treating an organic waste liquid, only heat is utilized by combustion, and it has not been possible to separate and recover components in the waste liquid for effective use.

【0004】特公平5−25276号公報には、有機性
汚泥の処理に当り、汚泥を高温高圧分解し、有機溶媒で
燃料回収する方法が提案されているが、この方法では、
可燃性液体が回収されているのみで、その他の成分の分
離回収はできなかった。
Japanese Patent Publication No. 5-25276 proposes a method of treating organic sludge by decomposing sludge at high temperature and pressure and recovering fuel with an organic solvent.
Only the flammable liquid was recovered, and other components could not be separated and recovered.

【0005】[0005]

【発明が解決しようとする課題】近年、廃棄物量の減容
化、資源の有効再利用が、あらゆる産業分野で要求され
ており、有機性廃液の処理に際しても、含有される有価
物を分離回収することが強く要望されている。
In recent years, reduction in volume of waste and effective reuse of resources have been required in all industrial fields, and even when treating organic waste liquids, valuable resources contained therein are separated and recovered. It is strongly desired to do so.

【0006】本発明は上記従来の実情に鑑みてなされた
ものであって、アンモニアイオン、無機酸イオン及び有
機物を含有する有機性廃液から、有価物を効率的に分離
回収する方法を提供することを目的とする。
The present invention has been made in view of the above-mentioned conventional circumstances, and provides a method for efficiently separating and recovering valuable resources from an organic waste liquid containing ammonia ions, inorganic acid ions, and organic substances. With the goal.

【0007】[0007]

【課題を解決するための手段】本発明の有機性廃液から
の有価物の回収方法は、アンモニアイオン、無機酸イオ
ン及び有機物を含有する有機性廃液から有価物を回収す
る方法において、該廃液にアルカリを添加した後、通気
によりアンモニアをガス化するアンモニアストリッピン
グ工程と、ガス化したアンモニアと無機酸水溶液とを接
触させてアンモニアを吸収させるアンモニア吸収工程
と、前記アンモニアストリッピング工程の流出液と有機
溶媒とを接触させて無機塩を析出させ、析出物を分離回
収する無機塩分離回収工程と、該無機塩分離回収工程の
分離液を加熱し、有機溶媒を気化分離するとともに有機
物溶液を回収する有機物回収工程と、該有機物回収工程
で気化した有機溶媒を液化し、前記無機塩分離回収工程
に送給する工程とを含む液化し、前記無機塩分離回収工
程に送給する工程とを含むことを特徴とする。
According to the present invention, there is provided a method for recovering valuable resources from an organic waste liquid, the method comprising recovering valuable resources from an organic waste liquid containing ammonia ions, inorganic acid ions and organic substances. After adding the alkali, an ammonia stripping step of gasifying ammonia by aeration, an ammonia absorbing step of contacting the gasified ammonia with an inorganic acid aqueous solution to absorb ammonia, and an effluent of the ammonia stripping step An inorganic salt is precipitated by contacting with an organic solvent, and an inorganic salt separating and recovering step of separating and recovering the precipitate, and the separated solution in the inorganic salt separating and recovering step is heated to vaporize and separate the organic solvent and collect the organic matter solution. An organic matter recovery step to be performed, and a step of liquefying the organic solvent vaporized in the organic matter recovery step and sending the liquefied organic solvent to the inorganic salt separation and recovery step. And no liquefaction, characterized in that it comprises a said inorganic salt separation and recovery sent to step Kyusuru process.

【0008】アンモニア除去後の液に有機溶媒を添加し
て無機塩の溶解度を下げて塩析することにより、無機塩
を効率的に分離することができる。無機塩を除去した液
から有機溶媒を気化分離することにより有機物を高濃度
で回収できる。
An inorganic solvent can be efficiently separated by adding an organic solvent to the solution from which ammonia has been removed to lower the solubility of the inorganic salt and performing salting out. The organic substance can be recovered at a high concentration by vaporizing and separating the organic solvent from the liquid from which the inorganic salt has been removed.

【0009】本発明においては、回収した無機塩を電気
分解して無機酸とアルカリとを生成させ、生じた無機酸
をアンモニア吸収工程に送給するとともに、アルカリを
アンモニアストリッピング工程に送給することが好まし
い。
In the present invention, the recovered inorganic salt is electrolyzed to generate an inorganic acid and an alkali, and the generated inorganic acid is sent to an ammonia absorbing step and the alkali is sent to an ammonia stripping step. Is preferred.

【0010】[0010]

【発明の実施の形態】以下図面を参照して本発明の実施
の形態を詳細に説明する。
Embodiments of the present invention will be described below in detail with reference to the drawings.

【0011】図1は本発明の有機性廃液からの有価物の
回収方法の実施の形態を示す系統図である。
FIG. 1 is a system diagram showing an embodiment of the method for recovering valuable resources from organic waste liquid according to the present invention.

【0012】なお、図1では、無機酸イオンとして硫酸
イオン(SO4 2- )を含む有機性廃液をアルカリとして
水酸化ナトリウム(NaOH)を用いて処理する場合を
例示したが、本発明は、何らこの方法に限定されるもの
ではなく、有機性廃液中の無機酸イオンの種類に特に制
限はない。
FIG. 1 shows a case where an organic waste liquid containing sulfate ions (SO 4 2− ) as inorganic acid ions is treated with sodium hydroxide (NaOH) as alkali. The method is not limited to this method, and the type of inorganic acid ions in the organic waste liquid is not particularly limited.

【0013】有機性廃液はまず混合槽1でアルカリ(N
aOH)を添加してpH10〜12程度に調整した後、
ストリッピング塔2で空気と向流接触させることによ
り、有機性廃液中のアンモニアイオンをアンモニアガス
として分離する。
First, the organic waste liquid is alkali (N) in a mixing tank 1.
aOH) to adjust the pH to about 10-12,
By bringing the stripping tower 2 into countercurrent contact with air, ammonia ions in the organic waste liquid are separated as ammonia gas.

【0014】図1の方法では、このアルカリとして、後
段の塩析槽5で得られた無機塩(Na2 SO4 )を電気
分解装置11で電気分解して得たNaOHを利用する
が、系外からのアルカリを用いても良い。
In the method of FIG. 1, NaOH obtained by electrolyzing an inorganic salt (Na 2 SO 4 ) obtained in the subsequent salting-out tank 5 with an electrolyzer 11 is used as the alkali. An external alkali may be used.

【0015】ストリッピング塔2で得られたアンモニア
ガスは吸収塔3で無機酸(H2 SO4 )水溶液と反応さ
せ、無機酸アンモニウム((NH4 2 SO4 )水溶液
として貯槽4に回収する。この無機酸水溶液量は、無機
酸アンモニウム生成の理論量程度で良い。
The ammonia gas obtained in the stripping tower 2 is reacted with an aqueous solution of an inorganic acid (H 2 SO 4 ) in the absorption tower 3 and is recovered in the storage tank 4 as an aqueous solution of an ammonium ammonium ((NH 4 ) 2 SO 4 ). . The amount of the inorganic acid aqueous solution may be about the theoretical amount of inorganic acid ammonium.

【0016】図1の方法では、この無機酸水溶液とし
て、後段の塩析槽5で得られた無機塩(Na2 SO4
を電気分解装置11で電気分解して得たH2 SO4 を利
用するが、系外からの無機酸水溶液を用いても良い。
In the method shown in FIG. 1, this inorganic acid aqueous solution is used as the inorganic salt (Na 2 SO 4 ) obtained in the subsequent salting-out tank 5.
H 2 SO 4 obtained by electrolyzing the compound in the electrolyzer 11 is used, but an inorganic acid aqueous solution from outside the system may be used.

【0017】一方、ストリッピング塔2の流出液は、塩
析槽5で有機溶媒が添加され、有機性廃液中の無機酸イ
オン(SO4 2-)と混合槽1で添加されたアルカリ(N
aOH)との反応で生成した無機塩(Na2 SO4 )が
塩析により分離除去される。
On the other hand, the effluent of the stripping tower 2 is added with an organic solvent in the salting-out tank 5, and the inorganic acid ions (SO 4 2− ) in the organic waste liquid and the alkali (N 2 ) added in the mixing tank 1 are added.
NaOH) and the resulting inorganic salt by reaction (Na 2 SO 4) is separated off by salting out.

【0018】ここで、有機溶媒の添加量は、無機塩濃
度、無機塩の種類、有機溶媒の種類、処理温度等によっ
ても異なるが、ストリッピング塔2の流出液に対して8
0〜120容積%程度とするのが好ましい。
The amount of the organic solvent to be added depends on the concentration of the inorganic salt, the type of the inorganic salt, the type of the organic solvent, the treatment temperature, etc.
It is preferred to be about 0 to 120% by volume.

【0019】本発明では、この有機溶媒として、後段の
気化器9で分離した有機溶媒を循環使用する。有機溶媒
としては、メタノール、エタノール、ジエチレングリコ
ールモノメチルエーテルなどを使用することができる。
In the present invention, as the organic solvent, the organic solvent separated in the latter vaporizer 9 is circulated and used. As the organic solvent, methanol, ethanol, diethylene glycol monomethyl ether and the like can be used.

【0020】塩析槽5で分離された無機塩(Na2 SO
4 )スラッジは遠心分離機6で脱水された後、貯槽7に
投入され、無機塩(Na2 SO4 )水溶液となる。
The inorganic salt (Na 2 SO) separated in the salting-out tank 5
4 ) After the sludge is dehydrated by the centrifugal separator 6, it is put into the storage tank 7 to become an inorganic salt (Na 2 SO 4 ) aqueous solution.

【0021】この無機塩(Na2 SO4 )水溶液は、電
気分解装置11に導入され、酸(H2 SO4 )とアルカ
リ(NaOH)とに電気分解される。また、電気分解で
生成した水(H2 O)は貯槽11に返送される。
This aqueous solution of an inorganic salt (Na 2 SO 4 ) is introduced into an electrolyzer 11 and electrolyzed into an acid (H 2 SO 4 ) and an alkali (NaOH). Water (H 2 O) generated by the electrolysis is returned to the storage tank 11.

【0022】塩析槽5の上澄水は、熱交換器8に導入さ
れ、次の気化器9で気化した有機溶媒と熱交換により予
熱された後、気化器9で加熱され、有機溶媒が気化分離
される。通常の場合、この加熱温度は90〜95℃程度
である。気化器9で気化した有機溶媒は、熱交換器8で
冷却された後、塩析槽5に送給される。
The supernatant water from the salting-out tank 5 is introduced into a heat exchanger 8 and is preheated by heat exchange with an organic solvent vaporized in a next vaporizer 9 and then heated in the vaporizer 9 to vaporize the organic solvent. Separated. Usually, this heating temperature is about 90 to 95 ° C. The organic solvent vaporized in the vaporizer 9 is cooled in the heat exchanger 8 and then sent to the salting-out tank 5.

【0023】有機溶媒の気化分離により有機物が濃縮さ
れた有機物溶液は、貯槽10に貯留される。この有機物
溶液は、有機性廃液からアンモニアイオンや無機酸イオ
ンが除去され、更に有機物が濃縮された、有機物を主体
とする溶液であり、肥料、飼料の原料等として再利用す
ることができる。
The organic substance solution in which the organic substance is concentrated by vaporization and separation of the organic solvent is stored in a storage tank 10. This organic substance solution is a solution mainly composed of organic substances obtained by removing ammonia ions and inorganic acid ions from the organic waste liquid and further concentrating the organic substances, and can be reused as a fertilizer, a raw material for feed, and the like.

【0024】このような本発明の有機性廃液からの有価
物の回収方法は、アンモニアイオンを10,000mg
/L以上、特に、30,000〜60,000mg/L
程度、SO4 2- 、Cl- 等の無機酸イオンを25,00
0mg/L以上、特に75,000〜150,000m
g/L程度、有機物をTOCとして20,000mg/
L以上、特に60,000〜120,000mg/L程
度含有する有機性廃液、例えば食品発酵廃液、調味料等
の食品製造廃液、医薬品製造廃液等からの有価物の分離
回収、再利用に極めて有効である。
In the method for recovering valuable resources from the organic waste liquid of the present invention, the method for recovering 10,000 mg of ammonia ions
/ L or more, especially 30,000-60,000 mg / L
About 25,000 inorganic acid ions such as SO 4 2− and Cl 2 −.
0 mg / L or more, especially 75,000 to 150,000 m
g / L, and 20,000 mg / TOC of organic matter as TOC.
L or more, especially about 60,000 to 120,000 mg / L, which is extremely effective in separating and recovering and reusing valuable resources from food production waste liquids such as food fermentation waste liquids, food production waste liquids such as seasonings, pharmaceutical production waste liquids, and the like. It is.

【0025】[0025]

【実施例】以下に実施例を挙げて本発明をより具体的に
説明する。
The present invention will be described more specifically with reference to the following examples.

【0026】実施例1 下記水質の有機性廃液(アミノ酸製造プロセスからの発
酵廃液)を図1に示す方法により処理した。
Example 1 The following organic wastewater having the following water quality (fermentation wastewater from the amino acid production process) was treated by the method shown in FIG.

【0027】有機性廃液水質 TOC: 110,000mg/L SO4 : 138,000mg/L NH4 −N: 56,000mg/L まず、この有機性廃液を35L/minの流量で混合槽
1に導入し、後段の電気分解装置11からの20重量%
NaOH水溶液を20L/minの割合で添加してpH
を11とした後、ストリッピング塔2に55L/min
で送給し、空気通気量160m3 /minでアンモニア
をガス化した。アンモニアガスは吸収塔3に送給し、後
段の電気分解装置11からの25重量%H2 SO4 水溶
液25L/minに吸収させて、26重量%濃度の(N
4 2 SO4 水溶液を得た。
The organic waste water TOC: 110,000mg / L SO 4: 138,000mg / L NH 4 -N: 56,000mg / L is first introduced to the mixing tank 1 the organic wastewater at a flow rate of 35L / min 20% by weight from the subsequent electrolyzer 11
NaOH aqueous solution is added at a rate of 20 L / min to adjust pH.
Was set to 11, and 55 L / min was added to the stripping tower 2.
And ammonia was gasified at an air ventilation rate of 160 m 3 / min. The ammonia gas is fed to the absorption tower 3 and is absorbed by a 25% by weight aqueous H 2 SO 4 solution 25 L / min from the subsequent electrolyzer 11 to obtain a 26% by weight (N
An aqueous solution of H 4 ) 2 SO 4 was obtained.

【0028】吸収塔3の流出液は塩析槽5に35L/m
inで送給し、後段の熱交換器8からの有機溶媒(エタ
ノール)を35L/minで添加し、20℃でNa2
4スラッジ14kg/minを得た。この沈澱は、遠
心分離機6で濃縮した後、貯槽7に導入した。この貯槽
7には、電気分解装置11からH2 O6L/minが循
環され、槽内のNa2 SO4 濃度は35重量%に調整さ
れている。
The effluent of the absorption tower 3 is supplied to the salting-out tank 5 at 35 L / m.
in, the organic solvent (ethanol) from the heat exchanger 8 at the subsequent stage was added at 35 L / min, and Na 2 S was added at 20 ° C.
O 4 sludge of 14 kg / min was obtained. The precipitate was concentrated in a centrifuge 6 and then introduced into a storage tank 7. In the storage tank 7, 6 L / min of H 2 O is circulated from the electrolysis device 11, and the concentration of Na 2 SO 4 in the tank is adjusted to 35% by weight.

【0029】この35重量%Na2 SO4 水溶液は13
L/minで電気分解装置11に送給され、Na2 SO
4 はH2 SO4 とNaOHに電気分解され、各々、吸収
塔3、混合槽1に送給される。なお、電気分解装置には
30L/minのH2 Oが補給される。
The 35% by weight aqueous solution of Na 2 SO 4 contains 13
L / min to the electrolyzer 11 and Na 2 SO
4 is electrolyzed into H 2 SO 4 and NaOH and sent to the absorption tower 3 and the mixing tank 1, respectively. The electrolyzer is supplied with 30 L / min of H 2 O.

【0030】塩析槽5の流出液63L/minは次いで
熱交換器8で80℃に予熱された後、気化器9で95℃
に加熱され、含有される有機溶媒が除去されて濃縮され
る。気化器9で濃縮された有機物溶液30L/minは
貯槽10に貯留される。一方、有機溶媒は熱交換器8で
熱交換されて冷却された後、塩析槽5に返送される。
The effluent 63 L / min of the salting-out tank 5 is preheated to 80 ° C. in the heat exchanger 8 and then 95 ° C. in the vaporizer 9.
And the organic solvent contained therein is removed and concentrated. The organic substance solution 30 L / min concentrated in the vaporizer 9 is stored in the storage tank 10. On the other hand, the organic solvent is cooled by heat exchange in the heat exchanger 8 and then returned to the salting-out tank 5.

【0031】この処理により、下記水質の有機物溶液が
原水の有機性廃液に対して0.86t/tの割合で得ら
れた。
By this treatment, the following organic substance solution having the following water quality was obtained at a ratio of 0.86 t / t to the organic waste liquid of the raw water.

【0032】有機物溶液水質 TOC: 180,000mg/L SO4 : 8,000mg/L NH4 −N: 300mg/L また、Na2 SO4 の回収量は原水の有機性廃液に対し
て0.17t/tで回収率は90%であった。
Organic matter solution water quality TOC: 180,000 mg / L SO 4 : 8,000 mg / L NH 4 —N: 300 mg / L The amount of recovered Na 2 SO 4 is 0.17 t with respect to the organic waste liquid of raw water. The recovery was 90% in / t.

【0033】[0033]

【発明の効果】以上詳述した通り、本発明の有機性廃液
からの有価物の回収方法によれば、アンモニアイオン、
無機酸イオン及び有機物を含有する有機性廃液から、有
価物を効率的に分離回収することができ、その有効利用
を図ることができる。
As described in detail above, according to the method for recovering valuable resources from organic waste liquid of the present invention, ammonia ions,
Valuables can be efficiently separated and recovered from the organic waste liquid containing inorganic acid ions and organic substances, and their effective use can be achieved.

【0034】特に、請求項2の方法によれば、系内で回
収した無機塩を利用して効率的な処理を行える。
In particular, according to the method of the second aspect, an efficient treatment can be performed using the inorganic salt recovered in the system.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の有機性廃液からの有価物の回収方法の
実施の形態を示す系統図である。
FIG. 1 is a system diagram showing an embodiment of a method for recovering valuable resources from organic waste liquid of the present invention.

【符号の説明】[Explanation of symbols]

1 混合槽 2 ストリッピング塔 3 吸収塔 4,7,10 貯槽 5 塩析槽 6 遠心分離機 8 熱交換器 9 気化器 11 電気分解装置 DESCRIPTION OF SYMBOLS 1 Mixing tank 2 Stripping tower 3 Absorption tower 4,7,10 Storage tank 5 Salting-out tank 6 Centrifuge 8 Heat exchanger 9 Vaporizer 11 Electrolyzer

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 アンモニアイオン、無機酸イオン及び有
機物を含有する有機性廃液から有価物を回収する方法に
おいて、 該廃液にアルカリを添加した後、通気によりアンモニア
をガス化するアンモニアストリッピング工程と、 ガス化したアンモニアと無機酸水溶液とを接触させてア
ンモニアを吸収させるアンモニア吸収工程と、 前記アンモニアストリッピング工程の流出液と有機溶媒
とを接触させて無機塩を析出させ、析出物を分離回収す
る無機塩分離回収工程と、 該無機塩分離回収工程の分離液を加熱し、有機溶媒を気
化分離するとともに有機物溶液を回収する有機物回収工
程と、 該有機物回収工程で気化した有機溶媒を液化し、前記無
機塩分離回収工程に送給する工程とを含むことを特徴と
する有機性廃液からの有価物の回収方法。
1. A method for recovering valuable resources from an organic waste liquid containing ammonia ions, inorganic acid ions and organic substances, comprising: adding an alkali to the waste liquid, and gasifying ammonia by aeration, followed by an ammonia stripping step; An ammonia absorption step of bringing gasified ammonia into contact with an aqueous solution of an inorganic acid to absorb ammonia; and contacting the effluent of the ammonia stripping step with an organic solvent to precipitate an inorganic salt, and separating and collecting the precipitate. An inorganic salt separation and recovery step, an organic material recovery step of heating the separated liquid of the inorganic salt separation and recovery step, vaporizing and separating the organic solvent and recovering an organic substance solution, and liquefying the organic solvent vaporized in the organic substance recovery step, Feeding the waste to the inorganic salt separation and recovery step.
【請求項2】 請求項1の方法において、前記無機塩分
離回収工程で回収した無機塩を電気分解して無機酸とア
ルカリとを生成させ、この無機酸を前記アンモニア吸収
工程に送給するとともに、アルカリを前記アンモニアス
トリッピング工程に送給することを特徴とする有機性廃
液からの有価物の回収方法。
2. The method according to claim 1, wherein the inorganic salt recovered in the inorganic salt separation and recovery step is electrolyzed to generate an inorganic acid and an alkali, and the inorganic acid is supplied to the ammonia absorption step. And recovering valuable resources from the organic waste liquid by feeding alkali to the ammonia stripping step.
JP9286857A 1997-10-20 1997-10-20 Method for recovering valuable materials from organic waste liquid Pending JPH11114552A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9286857A JPH11114552A (en) 1997-10-20 1997-10-20 Method for recovering valuable materials from organic waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9286857A JPH11114552A (en) 1997-10-20 1997-10-20 Method for recovering valuable materials from organic waste liquid

Publications (1)

Publication Number Publication Date
JPH11114552A true JPH11114552A (en) 1999-04-27

Family

ID=17709934

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9286857A Pending JPH11114552A (en) 1997-10-20 1997-10-20 Method for recovering valuable materials from organic waste liquid

Country Status (1)

Country Link
JP (1) JPH11114552A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104058538A (en) * 2014-06-30 2014-09-24 北京阳光欣禾科技有限公司 Technology method for steam stripping deacidification and deamination of waste water
KR102118040B1 (en) * 2019-08-19 2020-06-02 에코매니지먼트코리아홀딩스 주식회사 Method of recovering ammonium sulfate from wastewater

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104058538A (en) * 2014-06-30 2014-09-24 北京阳光欣禾科技有限公司 Technology method for steam stripping deacidification and deamination of waste water
KR102118040B1 (en) * 2019-08-19 2020-06-02 에코매니지먼트코리아홀딩스 주식회사 Method of recovering ammonium sulfate from wastewater

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