JPS588593A - Anaerobic digesting treatment of waste liquid containing sulfate ion - Google Patents
Anaerobic digesting treatment of waste liquid containing sulfate ionInfo
- Publication number
- JPS588593A JPS588593A JP56105095A JP10509581A JPS588593A JP S588593 A JPS588593 A JP S588593A JP 56105095 A JP56105095 A JP 56105095A JP 10509581 A JP10509581 A JP 10509581A JP S588593 A JPS588593 A JP S588593A
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- ions
- iron
- anaerobic
- treatment
- 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
Links
Classifications
-
- Y02W10/12—
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は、硫酸イオンを含有する有機性廃液の嫌気性消
化処理方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for anaerobic digestion of organic wastewater containing sulfate ions.
嫌気性消化処理方法は、比較的高濃度の有機性廃液の処
理に用いられ、一般に嫌気性条件下に反応温度30〜4
0℃付近で処理する方法(中温発酵法)と嫌気性条件下
に反応温度55〜60℃付近で処理する方法(高温発酵
法〕とがある。嫌気性消化方法では、被処理液中の有機
物がまず酢酸、プロピオン酸などの揮発性脂肪酸に分解
され(液化反応)、次に生成した揮発性脂肪酸が可燃性
メタンガスまで分解される丸め、エネルギー回収方法と
して優れている。The anaerobic digestion treatment method is used to treat organic wastewater with relatively high concentration, and is generally performed under anaerobic conditions at a reaction temperature of 30 to 40%.
There are two methods: a method of processing at around 0°C (medium temperature fermentation method) and a method of processing under anaerobic conditions at a reaction temperature of around 55 to 60°C (high temperature fermentation method).In the anaerobic digestion method, organic matter in the liquid to be treated is is first decomposed into volatile fatty acids such as acetic acid and propionic acid (liquefaction reaction), and then the volatile fatty acids produced are decomposed into flammable methane gas, making it an excellent energy recovery method.
しかしながら、この嫌気性消化処理の被処理液中に硫酸
イオンが含有されている場合は、消化槽内に生息する硫
酸還元菌の作用により、被処理液中の硫酸イオンが還元
され、硫黄イオンとして消化液中に溶存する。この硫黄
イオンは発生ガス中に腐蝕性の硫化水素として排出され
るが、被処理液中の硫酸イオンが比較的多く含有される
場合には、硫黄イオ°ンを硫化水素として系外に排出し
ても、なお嫌気性消化処理に阻害性を示す濃度(め1’
oom/%以上)の硫黄イオンが存在し、このため良好
な嫌気性処理が行われないという欠点がある。However, if sulfate ions are contained in the liquid to be treated during this anaerobic digestion treatment, the sulfate ions in the liquid to be treated are reduced by the action of sulfate-reducing bacteria living in the digestion tank, and converted into sulfur ions. Dissolved in digestive juices. These sulfur ions are discharged into the generated gas as corrosive hydrogen sulfide, but if the liquid to be treated contains a relatively large amount of sulfate ions, the sulfur ions are discharged from the system as hydrogen sulfide. However, concentrations that still inhibit anaerobic digestion (Me1'
oom/%) of sulfur ions, which prevents good anaerobic treatment.
従来、このような被処理液に対して、例えばカルンウム
などを添加し、硫酸イオンを硫酸カルシウムとして沈殿
分離する嫌気性消化処理の前処理方法が試みられている
が、このような方法では硫酸イオンを十分に除去するこ
とができず、良好な処理効果は得られなかった。また他
の方法として、消化槽内に塩素ガスを投入し、硫酸還元
菌の作用を抑制する方法も検討されたが、同時に生息し
ている他の嫌気性細菌への影響、および塩素ガスの注入
量の設定など種々の問題があり、実用化するまでには到
っていない。Conventionally, pretreatment methods for anaerobic digestion treatment have been attempted, in which sulfate ions are precipitated and separated as calcium sulfate by adding, for example, carunium to such liquids to be treated. could not be removed sufficiently, and good treatment effects could not be obtained. Another method was considered to suppress the action of sulfate-reducing bacteria by injecting chlorine gas into the digester, but there were concerns about the impact on other anaerobic bacteria living at the same time, and the injection of chlorine gas. There are various problems such as setting the amount, and it has not been put into practical use yet.
本発明の目的は、前記従来技術の欠点を解消し、嫌気性
処理に阻害性を示す硫酸または硫黄イオンを除去し、効
率よく嫌気性消化処理を行うことができる有機性廃液の
嫌気性消化処理方法を提供することにある。An object of the present invention is to provide an anaerobic digestion treatment for organic waste liquid, which eliminates the drawbacks of the prior art, removes sulfuric acid or sulfur ions that inhibit anaerobic treatment, and allows efficient anaerobic digestion treatment. The purpose is to provide a method.
本発明は、嫌気性消化槽内に存在する硫黄形態が不溶解
性の硫化鉄として存在する場合は嫌気性消化処理に阻害
性を示さないことに着目し、被処理液中の硫酸イオンを
鉄−硫黄化合物とする手段として、鉄を陽極板とし、不
溶解性の極板、例えば炭素板を陰極として、構成された
電解処理装置を嫌気性消化処理槽に付設し、被処理液を
電解処理装置に通じて処理t、被処理液中に鉄イオ・を
溶出させた後嫌気性消化処理し、該消化槽内の硫黄形態
を不溶解性の硫化鉄としキ除去するようにしたものであ
る。The present invention focuses on the fact that when the sulfur present in the anaerobic digestion tank exists in the form of insoluble iron sulfide, it does not inhibit anaerobic digestion treatment. - As a means of converting the liquid into sulfur compounds, an electrolytic treatment device configured with iron as an anode plate and an insoluble electrode plate, such as a carbon plate as a cathode, is attached to an anaerobic digestion treatment tank, and the liquid to be treated is electrolytically treated. After leaching iron ions into the treated liquid through a treatment device, anaerobic digestion is performed to remove the sulfur in the digestion tank as insoluble iron sulfide. .
すなわち本発明による嫌気性消化処理方法は、陽極に鉄
電極を有する電解処理装置を用い、被処理液中に嫌気性
消化処理で発生する硫黄イオンとの反応に必要な1〜2
倍当量の鉄イオンを電解処理時の電圧を調整して溶解さ
せた後、嫌気性消化処理を行うことを特徴とする。That is, the anaerobic digestion method according to the present invention uses an electrolytic treatment apparatus having an iron electrode as an anode, and uses 1 to 2 sulfur ions necessary for reaction with sulfur ions generated in the anaerobic digestion treatment in the liquid to be treated.
It is characterized by dissolving twice the equivalent amount of iron ions by adjusting the voltage during electrolytic treatment, and then performing anaerobic digestion treatment.
次に図面により本発明をさらに詳しく説明する。Next, the present invention will be explained in more detail with reference to the drawings.
第1図は、本発明に係る嫌気性消化を実施する装置の系
統図・である。被処理液は、先ず被処理液導入管12に
より鉄極板3(陽極)、炭素極板4(陰極)を設けた電
解処理槽2に導入され、通電により鉄イオンが被処理液
中に溶出される。この際、流入する被処理液中に嫌気性
消化処理で発生する硫酸イオンとの反応に必要な1〜2
倍当量の秩イオンが溶解するように直流変圧器13によ
り電圧が調整される。また電解処理槽2内は被処理液循
環ポンプ5および循環配管6を介して被処理液が循環さ
れ攪拌される。以上の処理により鉄イオンが溶解した被
処理液は、被処理液投入ポンプ7および連絡管8を介し
て嫌気性消化処理槽1に導入される。該消化処理槽l内
には嫌気性細菌、例えば液化菌、ガス化菌、硫酸還元菌
が生息しており、槽内の攪拌手段として攪拌用ガス配管
9、加温手段としてスチーム導入管10、および発生ガ
ス配管14、脱離液配管11が設けられている。FIG. 1 is a system diagram of an apparatus for carrying out anaerobic digestion according to the present invention. The liquid to be treated is first introduced into the electrolytic treatment tank 2 equipped with an iron electrode plate 3 (anode) and a carbon electrode plate 4 (cathode) through the liquid to be treated introduction pipe 12, and iron ions are eluted into the liquid to be treated by applying electricity. be done. At this time, 1 to 2
The voltage is adjusted by the DC transformer 13 so that double equivalent amount of Chichi ions are dissolved. Further, the liquid to be treated is circulated and stirred inside the electrolytic treatment tank 2 via the liquid to be treated circulation pump 5 and the circulation piping 6. The liquid to be treated in which iron ions have been dissolved by the above-described process is introduced into the anaerobic digestion tank 1 via the liquid to be treated pump 7 and the communication pipe 8 . Anaerobic bacteria, such as liquefaction bacteria, gasification bacteria, and sulfate-reducing bacteria, live in the digestion tank l, and there are a stirring gas pipe 9 as a stirring means in the tank, a steam introduction pipe 10 as a heating means, Also, a generated gas pipe 14 and a desorbed liquid pipe 11 are provided.
このような構成において、消化槽l内に導入された被処
理液は嫌気性消化処理により分解され、メタンガスおよ
び炭酸ガスとなり、一方、硫酸イオンは硫酸還元菌の作
用を受は硫黄イオンとなる。In such a configuration, the liquid to be treated introduced into the digestion tank 1 is decomposed by anaerobic digestion and becomes methane gas and carbon dioxide gas, while sulfate ions are affected by sulfate-reducing bacteria and become sulfur ions.
この硫黄イオンは被処理液中に溶解した鉄イかりと反応
し、槽内に硫化鉄が析出する。These sulfur ions react with iron ions dissolved in the liquid to be treated, and iron sulfide is precipitated in the tank.
次に第2図は、第1表に示すような性状の有機性廃液を
本発明方法およびカルシウムによる沈殿分離方法により
約30日間連続処理した結果宝示すものである。図中、
已5は本発明方法の場合、16はカルシウム沈殿方法の
場合、17は無処理の場合の結果をそれぞれ示す・
第 1 表
図から明らかなように、無処理a7>の場合、実験開始
後、約1・6日目でガスの発生がほとんど停止し、また
カルシウム沈殿方法tteの場合も、発生ガスは徐々に
低下し、30日経過後には20ONt/〜−゛vS程度
となるが、本発明の場合αりは、発生fjx量ハ500
〜60 ONt/に−VS と極メチ多く、また消化
槽内の硫黄イオンの増加も認められなかった。また発生
ガス中の硫化水素も他の二法に比べ低濃度に維持される
ことが明らかであシ、本発明方法によシ硫化水素ガスの
発生が抑制されることが分った。Next, FIG. 2 shows the results of continuous treatment for about 30 days of organic waste liquid having the properties shown in Table 1 using the method of the present invention and the precipitation separation method using calcium. In the figure,
5 shows the results for the method of the present invention, 16 shows the results for the calcium precipitation method, and 17 shows the results for no treatment. As is clear from Table 1, in the case of no treatment a7>, after the start of the experiment, Gas generation almost stops after about 1 to 6 days, and even in the case of the calcium precipitation method, the gas generation gradually decreases to about 20ONt/~-゛vS after 30 days, but the present invention In the case of α, the generated fjx amount is 500
-VS was extremely high at ~60 ONt/, and no increase in sulfur ions in the digester was observed. It is also clear that hydrogen sulfide in the generated gas is maintained at a lower concentration than the other two methods, and it has been found that the method of the present invention suppresses the generation of hydrogen sulfide gas.
以上、本発明によれば、嫌気性消化処理に阻害性を示す
硫黄イオンを除去し、効率のよい嫌気性処理を行うこと
ができる。As described above, according to the present invention, sulfur ions that inhibit anaerobic digestion treatment can be removed and efficient anaerobic treatment can be performed.
第1図は、本発明による硫酸イオン含有廃液の嫌気性消
化処理方法の一実施例を示す装置系統図、第2図は、本
発明方法の実施例の結果を示す図である。
1・・・嫌気性消化槽、 2・・・電解処理槽、3
・・・鉄極板、 4・・・炭素極板、12・・
・被処理液導入管。FIG. 1 is an apparatus system diagram showing an example of the method for anaerobic digestion of sulfate ion-containing waste liquid according to the present invention, and FIG. 2 is a diagram showing the results of the example of the method of the present invention. 1... Anaerobic digestion tank, 2... Electrolysis treatment tank, 3
... Iron plate, 4... Carbon plate, 12...
・Introduction pipe for liquid to be treated.
Claims (1)
陽極)および不溶解性電極(陰性)を有、する電気分解
装置に通水して処理し、被処理液中の硫酸イオンとの反
応に必要な当量以上の鉄イオンを溶解させた後、嫌気性
消化処理装置に導入し、該処理液中の硫黄形態を難溶解
性鉄−硫黄化合物に転化することを特徴とする硫酸イオ
ン含有廃液の嫌気性消化処理方法。fi+ Organic waste liquid containing sulfate ions is passed through an iron electrode (
Water is passed through an electrolyzer having an anode (anode) and an insoluble electrode (negative) to dissolve iron ions in excess of the equivalent amount required for reaction with sulfate ions in the liquid to be treated, followed by anaerobic treatment. 1. A method for anaerobic digestion of sulfate ion-containing waste liquid, which comprises introducing the sulfur ion-containing waste liquid into an anaerobic digestion apparatus and converting the sulfur form in the treated liquid into a hardly soluble iron-sulfur compound.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56105095A JPS588593A (en) | 1981-07-07 | 1981-07-07 | Anaerobic digesting treatment of waste liquid containing sulfate ion |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56105095A JPS588593A (en) | 1981-07-07 | 1981-07-07 | Anaerobic digesting treatment of waste liquid containing sulfate ion |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS588593A true JPS588593A (en) | 1983-01-18 |
Family
ID=14398344
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP56105095A Pending JPS588593A (en) | 1981-07-07 | 1981-07-07 | Anaerobic digesting treatment of waste liquid containing sulfate ion |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS588593A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6388099A (en) * | 1986-10-02 | 1988-04-19 | Zenzo Shimada | Pretreatment in methane fermenting method |
FR2675057A1 (en) * | 1991-03-22 | 1992-10-16 | Joassin Luc | Process and reactant for in-situ desulphurisation of biogas and for the elimination of corrosion and nauseating odour problems in anaerobic digesters and in any other mixtures or plants producing them |
CN117228839A (en) * | 2023-11-10 | 2023-12-15 | 重庆大学 | Integrated synchronous denitrification and desulfurization device and sewage treatment method |
-
1981
- 1981-07-07 JP JP56105095A patent/JPS588593A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6388099A (en) * | 1986-10-02 | 1988-04-19 | Zenzo Shimada | Pretreatment in methane fermenting method |
FR2675057A1 (en) * | 1991-03-22 | 1992-10-16 | Joassin Luc | Process and reactant for in-situ desulphurisation of biogas and for the elimination of corrosion and nauseating odour problems in anaerobic digesters and in any other mixtures or plants producing them |
CN117228839A (en) * | 2023-11-10 | 2023-12-15 | 重庆大学 | Integrated synchronous denitrification and desulfurization device and sewage treatment method |
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