JPH0116557B2 - - Google Patents

Info

Publication number
JPH0116557B2
JPH0116557B2 JP56103660A JP10366081A JPH0116557B2 JP H0116557 B2 JPH0116557 B2 JP H0116557B2 JP 56103660 A JP56103660 A JP 56103660A JP 10366081 A JP10366081 A JP 10366081A JP H0116557 B2 JPH0116557 B2 JP H0116557B2
Authority
JP
Japan
Prior art keywords
human waste
heat
fermentation
housing
heat exchanger
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
Application number
JP56103660A
Other languages
Japanese (ja)
Other versions
JPS586280A (en
Inventor
Tomio Suzuki
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.)
NISHIHARA KANKYO EISEI KENKYUSHO KK
Original Assignee
NISHIHARA KANKYO EISEI KENKYUSHO KK
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 NISHIHARA KANKYO EISEI KENKYUSHO KK filed Critical NISHIHARA KANKYO EISEI KENKYUSHO KK
Priority to JP56103660A priority Critical patent/JPS586280A/en
Publication of JPS586280A publication Critical patent/JPS586280A/en
Publication of JPH0116557B2 publication Critical patent/JPH0116557B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Fertilizers (AREA)

Description

【発明の詳細な説明】 この発明は、乾燥およびこれに続く発酵によつ
てし尿を効率よく処理する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for efficiently treating human waste by drying and subsequent fermentation.

し尿の処理方法として、消化、脱窒、硝化を含
む生物処理が多く採用されているが、この処理の
ためには大きい面積を必要とするので立地条件上
の制約が多く、また処理が不安定であるなどの問
題があつた。またし尿を直接乾燥する方法も各種
のものが提案されているが、いずれもランニング
コストが高く、排ガスの処理も難しいなどの理由
のために、実用化には至つていない。
Biological treatment, including digestion, denitrification, and nitrification, is often adopted as a method for treating human waste, but this treatment requires a large area, so there are many restrictions due to location conditions, and the treatment is unstable. There were problems such as: Various methods have also been proposed for directly drying human waste, but none have been put into practical use due to high running costs and difficulty in processing exhaust gas.

この発明は、し尿を乾燥させたのち発酵させる
ことにより、高い効率で処理できるとともに、排
ガスの処理の問題がなく、ランニングコストも安
い処理方法を提供することを目的としている。
The object of the present invention is to provide a processing method that can be processed with high efficiency by drying human waste and then fermenting it, without the problem of processing exhaust gas, and with low running costs.

つぎにこの発明方法の工程の一例について図面
を参照して説明する。図中に符号1で示す乾燥機
は、密閉されたハウジング2を有し、その内部
に、適当な液面を保持するようにし尿が収容され
る。またハウジング2内には、水破な回転軸3に
所定の間隔で取付けられた多数の円板4が、その
一部だけがし尿の液面下に位置した状態で配置さ
れている。この円板4は、モータ5の動力で回転
軸3とともに回転することによつて、その表面に
し尿を付着させた状態で液面の上方に引き上げ、
これによつて液面積を増大させて乾燥効果を向上
させる。(攪拌工程)なお符号6はハウジング2
内にし尿を導入するためのパイプを示す。
Next, an example of the steps of the method of this invention will be explained with reference to the drawings. The dryer indicated by reference numeral 1 in the figure has a sealed housing 2, in which human waste is accommodated so as to maintain an appropriate liquid level. Further, inside the housing 2, a large number of discs 4 are installed at predetermined intervals on a water-damaged rotating shaft 3, with only a portion of the discs being located below the surface of the human waste. By rotating together with the rotary shaft 3 by the power of the motor 5, the disk 4 is pulled up above the liquid level with the human urine attached to its surface.
This increases the liquid area and improves the drying effect. (Stirring process) The code 6 is the housing 2.
A pipe for introducing human waste into the interior is shown.

また、上記し尿の攪拌と同時に、ハウジング2
内のし尿を乾燥するために、コンプレツサ7、加
熱器8、熱交換器9、減圧弁10、熱交換器11
および加熱器12からなるヒートポンプが設けら
れている。ハウジング2内のガスは、パイプ13
を通して抜き出され、熱交換器11,9および加
熱器12を経て、パイプ14を通してハウジング
2内に戻される。(し尿乾燥工程)一方、熱媒体
は、コンプレツサ7で加圧され、加熱器7でさら
に加熱されたのち熱交換器9に送られ、ここで排
ガスとの間で熱交換を行つたのち、減圧弁10を
通つて減圧される。この減圧によつて温度が低下
した熱媒体は、熱交換器11に入り、ここで排ガ
スとの熱交換によつて加熱され、コンプレツサ7
に戻される。
In addition, at the same time as stirring the human waste, the housing 2
In order to dry the human waste inside, a compressor 7, a heater 8, a heat exchanger 9, a pressure reducing valve 10, a heat exchanger 11 are installed.
A heat pump consisting of a heater 12 and a heater 12 is provided. The gas inside the housing 2 is passed through the pipe 13
It is extracted through the heat exchangers 11, 9 and the heater 12, and then returned into the housing 2 through the pipe 14. (Human waste drying process) On the other hand, the heat medium is pressurized by the compressor 7, further heated by the heater 7, and then sent to the heat exchanger 9, where it exchanges heat with the exhaust gas, and then is depressurized. The pressure is reduced through valve 10. The heat medium whose temperature has been lowered by this pressure reduction enters the heat exchanger 11, where it is heated by heat exchange with the exhaust gas, and is transferred to the compressor 7.
will be returned to.

すなわち排ガスは、熱交換器11を通る間にい
つたん冷却され、熱交換器9で加熱され、加熱器
9でさらに加熱されたのちハウジング2に戻ると
いう経路を通つて循環し、ハウジング2内のし尿
の乾燥に必要な熱を供給する。また熱交換器11
内で冷却されたときに生じた凝結水は、パイプ1
5を通して取出され、受器16に収容される。
That is, the exhaust gas is cooled once while passing through the heat exchanger 11, heated by the heat exchanger 9, further heated by the heater 9, and then returned to the housing 2. Provides the heat necessary to dry human waste. Also, the heat exchanger 11
Condensed water generated when cooled inside pipe 1
5 and stored in a receiver 16.

一方、ハウジング2内で乾燥された濃縮し尿
は、パイプ17を経て発酵槽18に移送される。
ハウジング2から取出される濃縮し尿は、濃縮ケ
ーキ状(自由流動性をもたない程度のケーキ状)
のもので、発酵槽18内で好熱性細菌の作用で発
酵することによつて堆肥化する。(発酵工程)生
成したコンポストは、パイプ19を通して外部に
取出され、また一部はパイプ20を経て発酵槽1
8内に返送される。
On the other hand, concentrated human waste dried within the housing 2 is transferred to a fermentation tank 18 via a pipe 17.
The concentrated human waste taken out from the housing 2 is in the form of a concentrated cake (a cake-like form that does not have free-flowing properties).
It is composted by fermentation in the fermenter 18 under the action of thermophilic bacteria. (Fermentation process) The generated compost is taken out to the outside through the pipe 19, and some of it passes through the pipe 20 to the fermentation tank 1.
It will be returned within 8 days.

また発酵槽18内には、発酵による異常な温度
上昇を抑制するために、パイプ21を通して空気
が送り込まれる。そしてこの空気は、発酵槽18
内で加熱されたのち、パイプ22を通して加熱器
8および12に送られる。(発酵熱利用工程)好
熱性細菌による発酵は一般に70℃にも達する高温
で行われるので、発酵中の濃縮し尿と接触したの
ちパイプ22から取出された空気は充分に高い温
度、たとえば約50℃〜60℃となり、コンプレツサ
7で圧縮された熱媒体、および熱交換器9からハ
ウジング2に送られるガスをそれぞれ加熱器8お
よび12で加熱するための熱源として充分な熱量
を有している。一例を挙げると、ハウジング2か
らパイプ13を通して取出した約30℃の排ガス
は、熱交換器11を通過する間に約15℃まで冷却
されたが、熱交換器9および加熱器12を通るこ
とによつて約40℃まで加熱された。
Furthermore, air is fed into the fermentation tank 18 through a pipe 21 in order to suppress abnormal temperature rise due to fermentation. And this air is the fermenter 18
After being heated inside, it is sent to heaters 8 and 12 through pipe 22. (Fermentation heat utilization process) Fermentation by thermophilic bacteria is generally carried out at a high temperature of as high as 70°C, so the air taken out from the pipe 22 after coming into contact with the concentrated human waste during fermentation has a sufficiently high temperature, for example, about 50°C. ~60°C, and has a sufficient amount of heat as a heat source for heating the heat medium compressed by the compressor 7 and the gas sent from the heat exchanger 9 to the housing 2 by the heaters 8 and 12, respectively. For example, exhaust gas at about 30° C. taken out from the housing 2 through the pipe 13 was cooled to about 15° C. while passing through the heat exchanger 11, but instead of passing through the heat exchanger 9 and the heater 12. Thus, it was heated to about 40°C.

なお上記の実施例では、2つの加熱器8および
12を設けて省エネルギをはかつたが、いずれか
一方もしくは両方を省略してもよい。
In the above embodiment, two heaters 8 and 12 are provided to save energy, but one or both may be omitted.

また乾燥機1における乾燥処理に先立つて、し
尿をあらかじめ酸化処理しておけば、殺菌が行わ
れるとともに悪臭物質も除去されるので、取扱い
が容易になる。この酸化は、一般的には数日間の
ばつ気処理によつて行うことができるが、オゾ
ン、塩素等の酸化剤を用いてもよい。
Furthermore, if the human waste is oxidized in advance before drying in the dryer 1, it will be sterilized and odor substances will be removed, making it easier to handle. This oxidation can generally be carried out by an aeration treatment for several days, but an oxidizing agent such as ozone or chlorine may also be used.

以上のように、この発明によれば、攪拌工程
と、し尿乾燥工程と、発酵工程と、発酵熱利用工
程とを経ることにより、し尿の乾燥および堆肥化
を密閉系で行うことができる。このため臭気性の
排ガスが大気中に多量に放出されることはなく、
また熱の回収、再利用が容易でエネルギの消費量
が少なくてすむ。さらに乾燥は100℃以下の低温
で行われるので、発生するガスはアンモニアおよ
び水蒸気がほとんどであり、この発生ガスは化学
的な処理だけで容易に処理できる。また乾燥によ
つて得られた濃縮し尿は、乾燥中にアンモニアを
除去されているので、悪臭がなく、したがつて発
酵処理の際にも悪臭を発するおそれが少ない。し
かも添加物は添加されないので有機物含有率が高
く、発酵の際の発熱量が大きい。このためコンポ
ストの一部を発酵槽に返送するだけで所定の発酵
を行うことができ、オガクズ等の添加を必要とし
ない。なおし尿の乾燥は低温で行われるので、大
腸菌等の殺菌は不充分であるが、発酵処理時に殺
菌が行われるので問題はない。
As described above, according to the present invention, human waste can be dried and composted in a closed system through the stirring process, human waste drying process, fermentation process, and fermentation heat utilization process. This prevents large amounts of odorous exhaust gas from being released into the atmosphere.
In addition, heat can be easily recovered and reused, resulting in less energy consumption. Furthermore, since drying is performed at a low temperature of 100° C. or lower, most of the gases generated are ammonia and water vapor, and this gas can be easily treated by chemical treatment alone. In addition, since ammonia is removed from the concentrated human waste obtained by drying, there is no bad odor and there is little risk of emitting a bad odor during fermentation. Moreover, since no additives are added, the organic matter content is high and the amount of heat generated during fermentation is large. Therefore, the desired fermentation can be carried out simply by returning a portion of the compost to the fermentation tank, and there is no need to add sawdust or the like. Since human urine is dried at low temperatures, sterilization of Escherichia coli and the like is insufficient, but this is not a problem since sterilization is carried out during the fermentation process.

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

図はこの発明方法の工程の一例を示すフローシ
ートである。 1……乾燥機、2……ハウジング、3……回転
軸、4……円板、7……コンプレツサ、8……加
熱器、9……熱交換器、10……減圧弁、11…
…熱交換器、12……加熱器、18……発酵槽。
The figure is a flow sheet showing an example of the steps of the method of this invention. DESCRIPTION OF SYMBOLS 1... Dryer, 2... Housing, 3... Rotating shaft, 4... Disc, 7... Compressor, 8... Heater, 9... Heat exchanger, 10... Pressure reducing valve, 11...
...Heat exchanger, 12... Heater, 18... Fermenter.

Claims (1)

【特許請求の範囲】[Claims] 1 密閉されたハウジング内に多数の回転円板を
設けた乾燥機内に処理すべきし尿を供給し、該し
尿を該回転円板で攪拌する攪拌工程と、この攪拌
工程が行われている上記ハウジングから抜き出し
たガスをヒートポンプの熱交換器で冷却し、この
冷却によつて生じた凝結水を除去したのち、該ヒ
ートポンプの他の熱交換器で100℃以下の温度に
加熱してから該ハウジング内に戻して、該加熱さ
れたガスによつて上記攪拌工程と同時に上記し尿
の乾燥を行うし尿乾燥工程と、このし尿乾燥工程
で乾燥された濃縮し尿を密閉された発酵槽内で発
酵させることにより堆肥化する発酵工程と、この
発酵工程で生じた熱を上記ヒートポンプの熱媒
体、または上記ハウジングに戻されるガスの加熱
に利用する発酵熱利用工程とを備えたし尿の乾燥
処理方法。
1. A stirring process in which human waste to be treated is supplied into a dryer having a large number of rotating disks in a sealed housing, and the human waste is stirred by the rotating disks, and the above-mentioned housing in which this stirring process is performed. The gas extracted from the heat pump is cooled by the heat exchanger of the heat pump, the condensed water generated by this cooling is removed, and then heated to a temperature of 100°C or less by another heat exchanger of the heat pump, and then released into the housing. A human waste drying step in which the heated gas is used to dry the human waste at the same time as the stirring step, and the concentrated human waste dried in this human waste drying step is fermented in a sealed fermentation tank. A method for drying human waste, comprising a fermentation step for composting, and a fermentation heat utilization step for using the heat generated in the fermentation step to heat the heat medium of the heat pump or the gas returned to the housing.
JP56103660A 1981-07-02 1981-07-02 Drying treatment of night soil Granted JPS586280A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56103660A JPS586280A (en) 1981-07-02 1981-07-02 Drying treatment of night soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56103660A JPS586280A (en) 1981-07-02 1981-07-02 Drying treatment of night soil

Publications (2)

Publication Number Publication Date
JPS586280A JPS586280A (en) 1983-01-13
JPH0116557B2 true JPH0116557B2 (en) 1989-03-24

Family

ID=14359935

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56103660A Granted JPS586280A (en) 1981-07-02 1981-07-02 Drying treatment of night soil

Country Status (1)

Country Link
JP (1) JPS586280A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60139398A (en) * 1983-12-28 1985-07-24 Nishihara Environ Sanit Res Corp Treatment of high concentration waste water

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS524576A (en) * 1975-07-01 1977-01-13 Usui Kokusai Sangyo Kk Method of bending thermoplastic resin pipe with small diameter
JPS5344363A (en) * 1976-09-28 1978-04-21 Mitsubishi Heavy Ind Ltd Process for producing sludge compost
JPS5362887A (en) * 1976-11-17 1978-06-05 Fuji Electric Co Ltd Fermentor
JPS5581773A (en) * 1978-12-15 1980-06-20 Matsushita Electric Works Ltd Evaporating treatment apparatus
JPS5581775A (en) * 1978-12-15 1980-06-20 Matsushita Electric Works Ltd Evaporating treatment apparatus
DE2903008A1 (en) * 1979-01-25 1980-07-31 Schering Ag METHOD FOR EVAPORATION AND, IF NECESSARY, RECOVERY OF WATER FROM AQUEOUS SOLUTIONS

Also Published As

Publication number Publication date
JPS586280A (en) 1983-01-13

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