JPS5826997B2 - Human waste processing method and device - Google Patents
Human waste processing method and deviceInfo
- Publication number
- JPS5826997B2 JPS5826997B2 JP54050706A JP5070679A JPS5826997B2 JP S5826997 B2 JPS5826997 B2 JP S5826997B2 JP 54050706 A JP54050706 A JP 54050706A JP 5070679 A JP5070679 A JP 5070679A JP S5826997 B2 JPS5826997 B2 JP S5826997B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- filtrate
- concentrator
- deodorizing furnace
- evaporator
- 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
Links
Landscapes
- Chimneys And Flues (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
Description
【発明の詳細な説明】 本発明はし尿の処理方法及び装置に関する。[Detailed description of the invention] The present invention relates to a method and apparatus for treating human waste.
し尿のろ液を濃縮した状態で焼却するために、焼却炉の
排ガスをし尿ろ液濃縮用の間接加熱熱交換機(スクラバ
ー濃縮機、蒸発機等)に加熱媒体として供給する場合、
焼却炉の排ガスをそのま\熱交換機に入れると、排ガス
の温度低下により排ガス中に含有されている無機塩類が
熱交換機内の伝熱面に付着堆積して熱交換効率が速やか
に低下するという問題が生ずる。In order to incinerate the human waste filtrate in a concentrated state, when the exhaust gas from the incinerator is supplied as a heating medium to an indirect heating heat exchanger (scrubber concentrator, evaporator, etc.) for concentrating the human waste filtrate,
If exhaust gas from an incinerator is directly fed into a heat exchanger, the inorganic salts contained in the exhaust gas will adhere to and accumulate on the heat transfer surface inside the heat exchanger due to the temperature drop in the exhaust gas, causing a rapid decrease in heat exchange efficiency. A problem arises.
又排ガスとし尿ろ液の間の熱交換が液ガス方式のため、
ガス側にスケールが付着すると、総括伝熱係数が急に低
下し、熱交換効率が低下するばかりでなく、塩類の酸化
作用により熱交換機が腐蝕焼損しやすい。In addition, because the heat exchange between exhaust gas and urine filtrate is a liquid gas method,
When scale adheres to the gas side, the overall heat transfer coefficient suddenly decreases, not only does the heat exchange efficiency decrease, but also the heat exchanger is susceptible to corrosion and burnout due to the oxidizing effect of salts.
本発明は上記問題を解決するため、焼却炉で発生した排
ガスに水スプレーを加えて無機塩類の凝固点まで減温し
て多湿ガス化すると共に、減温により無機塩類の蒸気及
びヒユームを固形化して無機塩類を除去し、無機塩類含
有量の減少した多湿排ガスをろ液濃縮用の濃縮機に力ロ
熱媒体として導入し、濃縮機で発生した悪臭ガスを脱臭
炉で焼却し、無機塩類含有量のほとんどない脱臭炉の排
ガスをろ液濃縮用の蒸発機に加熱媒体として直接導入し
、蒸発機で発生した悪臭ガスを前記脱臭炉で焼却し、熱
回収を効果的に行うようにしたことを特徴としており、
次に図面により説明する。In order to solve the above problems, the present invention adds water spray to the exhaust gas generated in the incinerator to reduce the temperature to the freezing point of the inorganic salts and turn it into a humid gas, and also solidifies the vapor and fume of the inorganic salts by reducing the temperature. After removing inorganic salts, the humid exhaust gas with a reduced inorganic salt content is introduced into a concentrator for filtrate concentration as a heat transfer medium, and the foul-smelling gas generated in the concentrator is incinerated in a deodorizing furnace to reduce the inorganic salt content. The exhaust gas from the deodorizing furnace, which has almost no gas, is directly introduced as a heating medium into the evaporator for concentrating the filtrate, and the malodorous gas generated in the evaporator is incinerated in the deodorizing furnace, thereby effectively recovering heat. It is characterized by
Next, it will be explained with reference to the drawings.
第1図において濃縮ろ液受槽3は第1室1と第2室2を
備え、第1室1にはパイプ4から常時一定レベルまでし
尿ろ液が供給されるようになっている。In FIG. 1, the concentrated filtrate receiving tank 3 includes a first chamber 1 and a second chamber 2, and the first chamber 1 is always supplied with human waste filtrate up to a certain level from a pipe 4.
第1室1内のし尿ろ液は底部に連通したポンプ5により
加圧され、バイブロをへてスクラバー濃縮機7の室8へ
供給される。The human waste filtrate in the first chamber 1 is pressurized by a pump 5 connected to the bottom, and is supplied to the chamber 8 of the scrubber concentrator 7 through a vibro.
このスクラバー濃縮機7は上下管寄せ9,10の部分で
上下端が開口した多数の水管11を備え、水管11は管
寄せ9の部分で室8に連通し、又下端の管寄せ10の部
分で下部の室12に連通し、室12はミストセパレータ
ー13に接続している。This scrubber concentrator 7 is equipped with a large number of water pipes 11 whose upper and lower ends are open at the upper and lower headers 9 and 10, and the water pipes 11 communicate with the chamber 8 at the header 9 and at the lower end of the header 10. The chamber 12 is connected to a mist separator 13.
水管11の群の外部空間の底部と連通ずるように、濃縮
機7の本体には多湿排ガス人口14と、排ガス出口15
と濃縮水出口16が設けてあり、又水管11外空間を左
右に分割する隔壁17が下部管寄せ10から上方へ突出
している。The main body of the concentrator 7 includes a humid exhaust gas outlet 14 and an exhaust gas outlet 15 so as to communicate with the bottom of the external space of the group of water pipes 11.
and a concentrated water outlet 16 are provided, and a partition wall 17 that divides the space outside the water pipe 11 into left and right sides projects upward from the lower header 10.
隔壁17の上部と入口14内には洗浄水スプレーノズル
18.19が取り付けてあり、これらのノズルはパイプ
20,21゜22をへてポンプ23の吐出口に接続し、
ポンプ23の吸込口は凝縮液受槽24の底部に連通して
いる。Wash water spray nozzles 18, 19 are installed in the upper part of the bulkhead 17 and in the inlet 14, and these nozzles are connected to the outlet of the pump 23 through pipes 20, 21, 22,
The suction port of the pump 23 communicates with the bottom of the condensate receiving tank 24 .
入口14はサイクロン74を有するダクト25をへて減
温無機塩類凝固分離機26の多湿排ガス出口27に接続
し、排ガス出口15はダクト28、送風機29をへて排
気筒71に接続し、凝縮水出口16はパイプ32をへて
受槽24に接続している。The inlet 14 is connected to a humid exhaust gas outlet 27 of a temperature-reduced inorganic salt coagulation separator 26 through a duct 25 having a cyclone 74, and the exhaust gas outlet 15 is connected to an exhaust pipe 71 through a duct 28 and a blower 29 to collect condensed water. The outlet 16 is connected to the receiving tank 24 through a pipe 32.
第1室1の底部はポンプ34、パイプ35をへて蒸発機
36の入口37に接続し、蒸発機36のろ液出口38は
パイプ39をへて第2室2に連通し、従って第2室2内
には濃縮ろ液がある。The bottom of the first chamber 1 is connected via a pump 34 and a pipe 35 to an inlet 37 of an evaporator 36, and the filtrate outlet 38 of the evaporator 36 communicates via a pipe 39 to the second chamber 2 and thus the second Inside chamber 2 is a concentrated filtrate.
第2室2の底部はポンプ40、パイプ41をへて焼却炉
42のアトマイザ−43に接続し、アトマイザ−43の
部分には別にエアーコンプレッサーに至るライン44が
接続しており、従ってし尿の濃縮ろ液はアトマイザ−4
3の部分から焼却炉42内に噴霧45となって噴出する
。The bottom of the second chamber 2 is connected to an atomizer 43 of an incinerator 42 through a pump 40 and a pipe 41, and a separate line 44 to an air compressor is connected to the atomizer 43, thus concentrating human waste. Filtrate is atomizer 4
The spray 45 is ejected from the part 3 into the incinerator 42.
焼却炉42には噴霧45を囲む火炎46を形成するバー
ナ47が取り付けてあり、この火炎46により焼却炉4
2内は700℃以上の雰囲気となり、噴霧45内に含ま
れている無機塩類は蒸発してヒユーム状となる。A burner 47 that forms a flame 46 surrounding the spray 45 is attached to the incinerator 42, and this flame 46 causes the incinerator 4 to
2 becomes an atmosphere of 700° C. or higher, and the inorganic salts contained in the spray 45 evaporate and become fume-like.
焼却炉42内の底部はし渣焼却炉48を形成しており、
入口49の部分から投入されたし渣は下降する火炎によ
り焼却される。The bottom of the incinerator 42 forms a residue incinerator 48,
The residue introduced from the inlet 49 is incinerated by the descending flame.
焼却炉42の出口50部分はまだ750℃程度の高温状
態であり、無機塩類はヒユーム状で存在しているが、こ
のヒユーム状の塩類は次工程の減温無機塩類凝固分離機
26により固形化して分離される。The outlet 50 of the incinerator 42 is still at a high temperature of about 750°C, and the inorganic salts are present in the form of a fume, but this fume-like salt is solidified by the reduced-temperature inorganic salt coagulation separator 26 in the next step. separated.
分離機26は底部に液溜51と塩類溜52を備え、底壁
から上方に起立した隔壁53と土壁から下方へ突出した
隔壁54により矢印で示す如く上下に蛇行する通路がで
きており、液溜51の上部と入口55内に冷却水スプレ
ーノズル56.57が取り付けてあり、各スプレーノズ
ル56.57はパイプ22をへてポンプ23の吐出口に
接続している。The separator 26 is equipped with a liquid reservoir 51 and a salt reservoir 52 at the bottom, and a passage that meanders up and down as shown by the arrow is formed by a partition wall 53 rising upward from the bottom wall and a partition wall 54 projecting downward from the earthen wall. Cooling water spray nozzles 56,57 are installed in the upper part of the liquid reservoir 51 and in the inlet 55, and each spray nozzle 56,57 is connected to the outlet of the pump 23 through the pipe 22.
焼却炉42からでた高温の排ガスは分離機26の部分で
スプレーノズル56.57から噴出する水により冷却さ
れ、出口27部分では約140℃まで温度が下がり、同
時に多湿排ガスとなる。The high-temperature exhaust gas discharged from the incinerator 42 is cooled at the separator 26 by water ejected from the spray nozzles 56, 57, and at the outlet 27 the temperature drops to about 140° C. and at the same time becomes humid exhaust gas.
排ガスの温度が分離機26内で急激に低下する際、温度
が220〜250℃以下に下降すると、無機塩類が固形
化して破線矢印で示す如く塩類溜52内に落下する。When the temperature of the exhaust gas rapidly decreases within the separator 26 and the temperature drops below 220 to 250°C, the inorganic salts solidify and fall into the salt reservoir 52 as shown by the broken line arrow.
集積した塩類は適宜コンベアー58上へ排出される。The accumulated salts are discharged onto a conveyor 58 as appropriate.
59はし渣排出用のコンベアーである。59 is a conveyor for discharging scum.
分離機26の出口27からは無機塩類をほとんど含まな
い低温の多湿排ガスが排出され、この多湿排ガスはサイ
クロン74を通過し、更に固形分が除去・された状態で
スクラバー濃縮機7の加熱用熱媒体として人口14の部
分から水管11外空間の底部へ入り、多数の水管11に
易い上昇し、隔壁17により方向を変えて下降し、出口
15の部分からダクト28、送風機29をへて排気筒7
1へ送られる。A low-temperature, humid exhaust gas containing almost no inorganic salts is discharged from the outlet 27 of the separator 26, and this humid exhaust gas passes through a cyclone 74, in which the solid content is removed and then heated by the scrubber concentrator 7. As a medium, it enters the bottom of the outside space of the water pipe 11 from the population 14, easily ascends into the many water pipes 11, changes direction by the partition wall 17 and descends, and passes from the outlet 15 through the duct 28 and the blower 29 to the exhaust pipe. 7
Sent to 1.
水管11内には第1室1から供給されたし尿ろ液が流下
し、流下中に水管外を通過中の多湿排ガスから蒸気の凝
縮する潜熱を受けて蒸発し、ミストセパレーター13の
部分から蒸気はダクト61をへて脱臭炉30へ供給され
、効率を上昇する為ダクト61の途中に真空機器(例え
ば送風機75)を設け、低温蒸発をさせる。The human waste filtrate supplied from the first chamber 1 flows down into the water pipe 11, and as it flows down, it receives the latent heat of steam condensation from the humid exhaust gas passing outside the water pipe and evaporates. is supplied to the deodorizing furnace 30 through a duct 61, and in order to increase efficiency, a vacuum device (for example, a blower 75) is provided in the middle of the duct 61 to evaporate at a low temperature.
濃縮液はバイブロ2をへて第1室1へ戻され管内の真空
度が大きい場合はバイブロ2の間に濃縮ろ液受槽3に流
送するポンプを設ける。The concentrated liquid is returned to the first chamber 1 through the vibro 2, and if the degree of vacuum in the tube is large, a pump is provided between the vibro 2 to send the concentrated filtrate to a receiving tank 3.
このようなサイクルを繰り返して第1室1内のし尿ろ液
の濃度は増加する。By repeating such a cycle, the concentration of the human waste filtrate in the first chamber 1 increases.
脱臭炉30と蒸発機36の概略構造を説明する。The general structure of the deodorizing furnace 30 and the evaporator 36 will be explained.
脱臭炉30は概ね焼却炉42と同じ構造を備えており、
64はバーナ、65は悪臭ガスノズル、66は排ガス出
口で、この出口66はダクト67をへて蒸発機36の排
ガス入口68に接続している。The deodorizing furnace 30 has roughly the same structure as the incinerator 42,
64 is a burner, 65 is a foul-smelling gas nozzle, and 66 is an exhaust gas outlet, which is connected to the exhaust gas inlet 68 of the evaporator 36 through a duct 67.
蒸発機36の排ガス出口69はバイブロ9a、排風機7
0をへて排気筒71に接続し、悪臭ガス(蒸気)出ロア
2はダクト73をへてノズル65に接続している。The exhaust gas outlet 69 of the evaporator 36 is connected to the vibro 9a and the exhaust fan 7.
0 to an exhaust pipe 71, and the malodorous gas (steam) output lower 2 is connected to a nozzle 65 via a duct 73.
第1図の蒸発機36はケース77に予熱器を内蔵してお
り、その人口37にパイプ35が接続し、出ロア9はパ
イプ80をへてケース上壁に設けた複数個の噴霧口81
内の噴霧ノズル97に接続している。The evaporator 36 in FIG. 1 has a built-in preheater in a case 77, a pipe 35 is connected to the preheater 37, and the outlet lower 9 passes through a pipe 80 to a plurality of spray ports 81 provided on the upper wall of the case.
It is connected to the spray nozzle 97 inside.
ケース77内には横形ドラム82が固定してあり、ドラ
ム82内には第2図、第3図の如く、多数の攪拌羽根車
83を有する軸84がドラム82の端壁85を液密を保
持した状態で貫通し、ドラム82外へ突出した軸端部は
軸受86により回転自在に支持され、軸84の一端に固
定したスプロケット87に駆動チェーン88が掛は渡し
てある。A horizontal drum 82 is fixed inside the case 77, and inside the drum 82, as shown in FIGS. 2 and 3, a shaft 84 having a large number of stirring impellers 83 connects an end wall 85 of the drum 82 to keep it liquid-tight. The end of the shaft that penetrates the drum 82 while being held and projects outside the drum 82 is rotatably supported by a bearing 86, and a drive chain 88 is hooked around a sprocket 87 fixed to one end of the shaft 84.
チェーン88の他端は減速モータのスプロケット(共に
図示せず)に掛は渡しである。The other end of the chain 88 is connected to a sprocket of a deceleration motor (both not shown).
各羽根車83は、軸84に固定した複数個の放射状支持
板89と、支持板89の外縁に固着した筒状のリム板9
0と、リム板90の外周面に固着した放射状の多数の羽
根91で構成されており、ドラム82の内周面にわずか
な隙間をへだて\対向している。Each impeller 83 includes a plurality of radial support plates 89 fixed to a shaft 84 and a cylindrical rim plate 9 fixed to the outer edge of the support plates 89.
0 and a large number of radial blades 91 fixed to the outer peripheral surface of the rim plate 90, and facing the inner peripheral surface of the drum 82 with a slight gap.
ドラム82の外周面には螺旋フィン92が固着してあり
、螺旋フィン92の外周縁はケース内筒93に当接して
、ケース内筒93とドラム82の間に螺旋状通路94を
形成し、この通路94の一端は排ガス入口68に接続し
、他端は排ガス出口69に接続している。A spiral fin 92 is fixed to the outer peripheral surface of the drum 82, and the outer peripheral edge of the spiral fin 92 contacts the case inner cylinder 93 to form a spiral passage 94 between the case inner cylinder 93 and the drum 82. One end of this passage 94 is connected to the exhaust gas inlet 68 and the other end is connected to the exhaust gas outlet 69.
ケース77とケース内筒93の間の空間の内、第2図の
如く隔壁94aで区画された下半部には断熱材95が充
填してあり、隔壁94aより上方の空間96の上端部に
噴霧口81の部分から噴霧ノズル97が下向きに突出し
ている。A heat insulating material 95 is filled in the lower half of the space between the case 77 and the case inner cylinder 93, which is partitioned by a partition wall 94a as shown in FIG. A spray nozzle 97 projects downward from the spray port 81.
空間96の下端部はパイプ98を介してドラム82内に
連通している。The lower end of the space 96 communicates with the inside of the drum 82 via a pipe 98.
装置の運転中、入口68から流入した高温の排ガスは螺
旋状通路94を旋回しながら通過し、排ガス出口69か
ら排出され、その間にドラム82及びケース内筒93に
熱を与える。During operation of the device, high-temperature exhaust gas flowing in from the inlet 68 passes through the spiral passage 94 while swirling and is discharged from the exhaust gas outlet 69, giving heat to the drum 82 and the case inner cylinder 93 during the operation.
一方ノズル97から空間96内へ噴射されたろ液はケー
ス内筒93上に付着し、液膜を形成して流れ落ち、ケー
ス内筒93から熱を受けて蒸発し、濃縮したろ液ト蒸気
はパイプ98をへてドラム82内に入る。On the other hand, the filtrate injected from the nozzle 97 into the space 96 adheres to the case inner cylinder 93, forms a liquid film and flows down, receives heat from the case inner cylinder 93 and evaporates, and the concentrated filtrate vapor is transferred to the pipe. 98 and enters the drum 82.
ドラム82内では複数個の羽根車83が高速で回転して
いるため、羽根91と共に回転するろ液はドラム82の
内面に遠心力で押し付けられ、液膜を形成し、ドラム8
2から熱を受けて蒸発し、濃縮した状態で出口38へ達
する。Since a plurality of impellers 83 are rotating at high speed inside the drum 82, the filtrate rotating together with the blades 91 is pressed against the inner surface of the drum 82 by centrifugal force, forming a liquid film, and the drum 8
It receives heat from 2, evaporates, and reaches the outlet 38 in a concentrated state.
ドラム82内で発生した悪臭ガスは出ロア2から前記脱
臭炉30へ供給される。The malodorous gas generated within the drum 82 is supplied from the outlet lower 2 to the deodorizing furnace 30.
以上説明したように第2室2内のし尿濃縮ろ液はアトマ
イザ−43の部分から焼却炉42内へ噴射されてそこで
焼却され、発生した高温の排ガスはそのままスクラバー
濃縮機7へ供給されるのではなく、一旦減温無機塩類凝
固分離機26内に入り、そこでスプレーノズル56,5
7から供給される冷却水により、入口55部分の約75
0℃から出口27部分の約140℃程度まで急激に減温
するようにしたので、220〜250°C以下に温度が
低下した時排ガス中の無機塩類が固形fヒして塩類溜5
2へ溜まる。As explained above, the concentrated filtrate of human waste in the second chamber 2 is injected from the atomizer 43 into the incinerator 42 and incinerated there, and the generated high-temperature exhaust gas is directly supplied to the scrubber concentrator 7. Instead, it enters the temperature-reduced inorganic salt coagulation separator 26, where the spray nozzles 56, 5
By cooling water supplied from 7, approximately 75
Since the temperature is rapidly reduced from 0°C to about 140°C at the outlet 27, when the temperature drops below 220 to 250°C, the inorganic salts in the exhaust gas become solid F and the salt reservoir 5
Accumulates to 2.
従って間接加熱式のスクラバー濃縮機7へ供給される排
ガスは概ね140℃の低温、しかも多湿のガスとなり、
スプレーノズル1819から添加される洗浄水の作用と
相俟って、多数の水管11の外表面に速やかに凝縮し、
濃縮機7内における熱交換が液々形式に近づき、総括伝
熱係数が大幅)と増力口して熱交換効率が向上する。Therefore, the exhaust gas supplied to the indirect heating scrubber concentrator 7 has a low temperature of approximately 140°C and is humid.
Combined with the action of the cleaning water added from the spray nozzle 1819, the water quickly condenses on the outer surfaces of the numerous water pipes 11,
The heat exchange in the concentrator 7 approaches a liquid-liquid type, and the overall heat transfer coefficient increases greatly) and the heat exchange efficiency improves.
又水管11の表面には無機塩類が付着しないため、伝熱
面の汚損、腐蝕とそれによる熱交換効率の低下を確実に
防止することができる。Furthermore, since inorganic salts do not adhere to the surface of the water pipe 11, it is possible to reliably prevent staining and corrosion of the heat transfer surface and the resulting decrease in heat exchange efficiency.
更に濃縮機7に供給される排ガス温度は充分低いため、
濃縮機7の焼損の恐れはなくなり、装置の耐久性が向上
する。Furthermore, since the temperature of the exhaust gas supplied to the concentrator 7 is sufficiently low,
There is no fear of burnout of the concentrator 7, and the durability of the device is improved.
濃縮機7で発生した悪臭ガスはミストセパレーター13
の部分からバイブロ1.送風機75(減圧装置)をへて
脱臭炉30に供給され、蒸発機36で発生した悪臭ガス
(蒸気)もダクト73をへて脱臭炉30へ供給されるの
で、全密閉形式で悪臭ガスを処理することができ、悪臭
公害の恐れはなくなる。The foul-smelling gas generated in the concentrator 7 is transferred to the mist separator 13.
Vibro 1 from the part. The malodorous gas (steam) generated in the evaporator 36 is supplied to the deodorizing furnace 30 through the blower 75 (pressure reducing device), and the malodorous gas (steam) generated in the evaporator 36 is also supplied to the deodorizing furnace 30 through the duct 73, so the malodorous gas is treated in a completely closed system. This eliminates the risk of odor pollution.
又焼却炉42の排ガス中の熱を濃縮機7で、又脱臭炉3
0の排ガス中の熱を蒸発機36でそれぞれ回収するよう
にしたので、熱効率が向上する。In addition, the heat in the exhaust gas from the incinerator 42 is transferred to the concentrator 7 and the deodorizing furnace 3.
Since the heat in the zero exhaust gas is recovered by the evaporator 36, thermal efficiency is improved.
このように本発明によると、煤塵を焼却炉42の部分で
一手に発生させ、発生した煤塵を分離機26、濃縮機7
の部分できれいに処理し、濃縮機7の部分で熱を回収し
、しかも悪臭ガスは脱臭炉30の部分で一手に処理し、
かつ脱臭炉30の熱は蒸発機36で回収するようにした
ので、悪臭公害を伴なうことなくし尿を効率よく処理す
ることができる。According to the present invention, soot and dust are generated all at once in the incinerator 42, and the generated soot and dust is transferred to the separator 26 and the concentrator 7.
The gas is treated cleanly in the concentrator 7, the heat is recovered in the concentrator 7, and the foul-smelling gas is treated in the deodorizing furnace 30.
Moreover, since the heat of the deodorizing furnace 30 is recovered by the evaporator 36, human waste can be efficiently processed without causing foul odor pollution.
第1図は本発明による装置の主要部を縦断面で示す構造
略図、第2図は第1図の蒸発機の垂直断面図、第3図は
一部を切欠いた斜視図である。
3・・・・・・濃縮ろ液受槽、7・・・・・・スクラバ
ー濃縮機、26・・・・・・減温無機塩類凝固分離機、
3o・・・・・・脱臭炉、36・・・・・・蒸発機、4
2・・・・・・焼却炉、72・・・・・・悪臭ガス出口
。FIG. 1 is a structural schematic diagram showing a main part of the apparatus according to the present invention in longitudinal section, FIG. 2 is a vertical sectional view of the evaporator of FIG. 1, and FIG. 3 is a partially cutaway perspective view. 3... Concentrated filtrate receiving tank, 7... Scrubber concentrator, 26... Temperature-reduced inorganic salt coagulation separator,
3o... Deodorizing furnace, 36... Evaporator, 4
2... Incinerator, 72... Offensive gas outlet.
Claims (1)
えて無機塩類の凝固点まで減温することにより固形化し
た塩類を除去した後、塩類含有量の減少した多湿排ガス
をろ液濃縮用の濃縮機に加熱媒体として導入し、濃縮機
で発生した悪臭ガスを脱臭炉で焼却し、脱臭炉の排ガス
をろ液濃縮用の蒸発機に加熱媒体として導入し、蒸発機
で発生した悪臭ガスを前記脱臭炉で焼却するようにした
ことを特徴とするし尿の処理方法。 2 濃縮ろ液受槽と、ろ液受槽内の濃縮ろ液を焼却する
焼却炉と、焼却炉の排ガスに対し水スプレーを加える減
温無機塩類凝固分離機と、分離機からの多湿排ガスを月
日熱媒体とするろ液濃縮用の濃縮機と、濃縮機で発生し
た悪臭ガスを焼却する脱臭炉と、脱臭炉の排ガスを加熱
媒体とするろ液濃縮用の蒸発機を備え、蒸発機の悪臭ガ
ス出口を脱臭炉に接続したことを特徴とするし尿の処理
装置。[Claims] 1. After incinerating the concentrated filtrate of human waste and removing solidified salts by adding water spray to the exhaust gas and reducing the temperature to the freezing point of inorganic salts, a humid exhaust gas with a reduced salt content is obtained. is introduced as a heating medium into a concentrator for concentrating the filtrate, the malodorous gas generated by the concentrator is incinerated in a deodorizing furnace, and the exhaust gas from the deodorizing furnace is introduced as a heating medium into an evaporator for concentrating the filtrate. A method for treating human waste, characterized in that the malodorous gas generated in the deodorizing furnace is incinerated. 2 A concentrated filtrate receiving tank, an incinerator that incinerates the concentrated filtrate in the filtrate receiving tank, a temperature-reducing inorganic salt coagulation separator that sprays water on the exhaust gas from the incinerator, and a humid exhaust gas from the separator. The evaporator is equipped with a concentrator for concentrating the filtrate that uses solar heating medium, a deodorizing furnace that incinerates the foul-smelling gas generated by the concentrator, and an evaporator for concentrating the filtrate that uses the exhaust gas of the deodorizing furnace as the heating medium. A human waste processing device characterized in that a foul-smelling gas outlet is connected to a deodorizing furnace.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54050706A JPS5826997B2 (en) | 1979-04-23 | 1979-04-23 | Human waste processing method and device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP54050706A JPS5826997B2 (en) | 1979-04-23 | 1979-04-23 | Human waste processing method and device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS55143314A JPS55143314A (en) | 1980-11-08 |
| JPS5826997B2 true JPS5826997B2 (en) | 1983-06-06 |
Family
ID=12866337
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP54050706A Expired JPS5826997B2 (en) | 1979-04-23 | 1979-04-23 | Human waste processing method and device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5826997B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62262794A (en) * | 1986-05-08 | 1987-11-14 | Shimizu Constr Co Ltd | Treatment of waste water |
-
1979
- 1979-04-23 JP JP54050706A patent/JPS5826997B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62262794A (en) * | 1986-05-08 | 1987-11-14 | Shimizu Constr Co Ltd | Treatment of waste water |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS55143314A (en) | 1980-11-08 |
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