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JPS6220875B2 - - Google Patents
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JPS6220875B2 - - Google Patents

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Publication number
JPS6220875B2
JPS6220875B2 JP629782A JP629782A JPS6220875B2 JP S6220875 B2 JPS6220875 B2 JP S6220875B2 JP 629782 A JP629782 A JP 629782A JP 629782 A JP629782 A JP 629782A JP S6220875 B2 JPS6220875 B2 JP S6220875B2
Authority
JP
Japan
Prior art keywords
acidic
water
basic substance
tank
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.)
Expired
Application number
JP629782A
Other languages
Japanese (ja)
Other versions
JPS58122086A (en
Inventor
Kunihiro Tsuruta
Tei Hikino
Yukiro Komai
Masahiro Indo
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co 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 Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP57006297A priority Critical patent/JPS58122086A/en
Publication of JPS58122086A publication Critical patent/JPS58122086A/en
Publication of JPS6220875B2 publication Critical patent/JPS6220875B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 本発明は、石油給湯機、ガス湯沸機等に於いて
潜熱交換を行う際に発生する酸性結露水の中和処
理機構に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a mechanism for neutralizing acidic condensed water generated during latent heat exchange in oil water heaters, gas water heaters, and the like.

近年、省エネルギーの観点より高効率な石油給
湯機、ガス湯沸機等の燃焼機器が必要とされ、燃
焼排ガス中に含まれる潜熱を回収する熱交換器を
有した燃焼機器が開発されてきた。しかしなが
ら、この潜熱回収用熱交換器の表面では、燃焼排
ガス中の二酸化炭素や窒素酸化物等を溶かしこん
だ酸性結露水が発生し、この酸性結露水をそのま
ま排出した場合、配管の腐食やコンクリートを溶
かす等の問題が起こるため、化学的に中和する中
和処理機構が必要となつてきた。
In recent years, there has been a need for highly efficient combustion appliances such as oil water heaters and gas water heaters from the perspective of energy conservation, and combustion appliances having heat exchangers that recover latent heat contained in combustion exhaust gas have been developed. However, on the surface of this latent heat recovery heat exchanger, acidic condensation water that dissolves carbon dioxide, nitrogen oxides, etc. in the combustion exhaust gas is generated, and if this acidic condensation water is discharged as it is, it may cause corrosion of pipes and concrete. Because of the problems such as dissolving the substances, a neutralization treatment mechanism that chemically neutralizes them has become necessary.

従来の中和処理機構は、単数又は複数の処理槽
に塩基性物質を設置し、順次に結露水を流して化
学処理するものであり、第1図に示す中和処理機
構が使用されていた。この中和処理機構は、ボデ
イー1に円板状の塩基性物質2を設置した処理槽
3を複数個設けたものであり、酸性結露水は結露
水入口4より流入し塩基性物質2と接触しながら
順次下流側へ流れを形成し、中和処理された水は
結露水出口5より排出されていた。この中和処理
機構において、処理槽3は複数個ずつ直列に傾斜
させて並べられ、この列が数段である構成であつ
た。このような処理槽における第1の問題点は処
理液の流れ方による中和能力の変動の問題であつ
た。すなわち従来の処理槽においては、堰堤流出
端に於いて酸性結露水の表面張力による水塊が発
生し、この水塊が表面張力と自重のバランスが崩
れた時急速に次槽に流入するため、将棋倒し的流
れが発生していた。そのため、定常的酸性結露水
の流入に対して間欠的流れを形成し、充分な反応
時間を保ためままに流れることから、酸度の高い
まま処理水出口部5より排出される幣害があつ
た。また、機構の取扱い時や輸送時等に塩基性物
質2が処理槽3から外れたりしないようにするた
め上壁6を設けてあるため、酸性結露水が正しく
滴下されるべき次段の最初の処理槽に入らず、上
壁を伝つて途中で滴下したり、そのまま次々段ま
で上壁を伝つて流れてしまうため、所定の処理が
されないまま酸度の高い結露水が排出される弊害
があつた。第2の問題点は塩基性物質2が、円板
状であるために酸性結露水と反応して溶解すると
表面積が小さくなり、溶解するにつれて中和能力
が低下していた。しかも酸性結露水の酸度が高い
注入口側の塩基性物質の反応量が出口側の塩基性
物質の反応量より大となり、注入口側の塩基性物
質の消耗が激しく、消滅するに至る。酸性結露水
の処理にはその酸度と流量に応じて必要とされる
処理段数Nおよび滞留時間を必要とすることか
ら、前段が消滅した分だけ後段に余分な段数をあ
らかじめ準備して、その必要段数を確保する必要
が生じ、所定の処理量の処理を実現するには必要
とされる処理段数Nだけ余分の段数を準備する必
要があり塩基性物質の量を必要以上に使用しなけ
ればならぬ無駄があると共に、機構を必要以上に
大きくする欠点があつた。又前述の反応におい
て、酸性結露水の処理が完了に必要とされる処理
段数N以後の段においては反応に寄与することな
しに塩基性物質が溶出する無駄も加わつて無駄の
大きいものであつた。第3の問題点は従来の中和
処理機構を石油給湯機、ガス湯沸機等に取り付け
て使用すると熱交換器の腐食生成物や空気中の塵
埃等の不溶性異物の混入により目詰りを起し中和
能力が低下し易いことであつた。これは塩基性物
質2が処理槽3と線接触、ボデイ1とは面接触し
ているためであつた。そのため、不溶性異物を混
入した結露水は、塩基性物質2と処理槽3および
ボデイ1の接触部にあたり、ここに不溶性異物が
堆積すると目詰まりをして流れなくなり中和能力
が低下していた。
Conventional neutralization treatment mechanisms install basic substances in one or more treatment tanks and perform chemical treatment by sequentially flowing dew water, and the neutralization treatment mechanism shown in Figure 1 was used. . This neutralization treatment mechanism has a body 1 equipped with a plurality of treatment tanks 3 in which disk-shaped basic substances 2 are installed, and acidic condensation water flows in from a condensation water inlet 4 and comes into contact with the basic substances 2. Meanwhile, a flow was formed sequentially to the downstream side, and the neutralized water was discharged from the dew condensation water outlet 5. In this neutralization processing mechanism, a plurality of processing tanks 3 are arranged in series in a tilted manner, and each row has several stages. The first problem with such a treatment tank is that the neutralization ability fluctuates depending on the flow direction of the treatment liquid. In other words, in conventional treatment tanks, a water mass is generated at the outflow end of the dam due to the surface tension of acidic condensed water, and when this water mass loses the balance between surface tension and its own weight, it rapidly flows into the next tank. A shogi-like situation was occurring. Therefore, an intermittent flow is formed in response to the steady inflow of acidic condensation water, and the water continues to flow to maintain sufficient reaction time, causing damage to the water as it is discharged from the treated water outlet 5 with high acidity. . In addition, an upper wall 6 is provided to prevent the basic substance 2 from falling out of the treatment tank 3 during handling or transportation of the mechanism, so that the first stage of the next stage where acidic condensation water should be dripped correctly is provided. Because the water does not enter the treatment tank and drips along the upper wall, or flows down the upper wall to one stage after another, there is a problem in that highly acidic condensed water is discharged without being treated as specified. . The second problem is that since the basic substance 2 has a disk shape, when it reacts with acidic condensation water and dissolves, the surface area decreases, and as it dissolves, the neutralization ability decreases. Moreover, the reaction amount of the basic substance on the inlet side, where the acidity of the acidic condensation water is high, is greater than the reaction amount of the basic substance on the outlet side, and the basic substance on the inlet side is rapidly consumed and disappears. Since the treatment of acidic condensed water requires the number of processing stages N and residence time required depending on its acidity and flow rate, an extra number of stages in the latter stage is prepared in advance to compensate for the disappearance of the previous stage. It becomes necessary to secure the number of stages, and in order to realize the treatment of the predetermined processing amount, it is necessary to prepare an extra number of stages equal to the required number of processing stages N, and the amount of basic substance must be used in excess of the necessary amount. This had the disadvantage of not only being wasteful but also making the mechanism larger than necessary. In addition, in the above-mentioned reaction, in the stages after the number of processing stages N required to complete the treatment of the acidic condensed water, there was also the waste of basic substances being eluted without contributing to the reaction, resulting in a large waste. . The third problem is that when conventional neutralization processing mechanisms are used in oil water heaters, gas water heaters, etc., they can become clogged due to insoluble foreign matter such as corrosion products in the heat exchanger and dust in the air. However, the neutralizing ability was likely to decrease. This was because the basic substance 2 was in line contact with the processing tank 3 and in surface contact with the body 1. Therefore, the condensed water mixed with insoluble foreign matter hits the contact area between the basic substance 2, the treatment tank 3, and the body 1, and when the insoluble foreign matter accumulates there, it becomes clogged and does not flow, reducing the neutralization ability.

本発明はかかる従来の問題点を解決した酸性結
露水の中和処理機構を提供するものである。すな
わち、本発明の目的は、(1)酸性結露水が酸度の高
いまま排出されることをなくし、確実に塩基性物
質と反応して常に中和処理されて排出されるこ
と、(2)塩基性物質が酸性結露水と反応して溶解
し、表面積が小さくなることによる中和能力の低
下を少なくすること、(3)熱交換器の腐食生成物や
空気中の塵埃等の不溶性異物による流路の目詰ま
りを起こしにくくし、中和能力が低下しにくくす
ること、である。
The present invention provides a mechanism for neutralizing acidic condensed water that solves these conventional problems. That is, the objects of the present invention are (1) to prevent acidic condensed water from being discharged with high acidity and to ensure that it reacts with basic substances and is always neutralized before being discharged; (3) To reduce the loss of neutralization ability due to the reaction of acidic substances with acidic condensation water and their dissolution, resulting in a smaller surface area; The aim is to make it difficult for the passages to become clogged and for the neutralization ability to be less likely to decline.

この目的を達成するために、本発明は、堰堤を
有する処理槽内に筒状塩基性物質を隙間を設けて
配置し、酸性結露水を上記塩基性物質の内管部へ
導き、内管部から外管部へ流して該塩基性物質と
接触させたのち、処理槽の堰堤より溢れて流出さ
せるような酸性結露水の流れを形成している。こ
の構成によつて、酸性結露水は、筒状塩基性物質
の内管部および外管部、底面部と接触して反応し
常に中和処理されて排出させる。一方、筒状塩基
性物質の内管部および外管部は酸性結露水と反応
して溶解するが、内管部は溶解するにつれて管内
径は増大し、外管部は溶解するにつれて管外径は
減少するため酸性結露水との接触面積の変化が少
なく、塩基性物質の溶解による中和能力の低下が
少ない。また、熱交換器の腐食生成物や空気中の
塵埃等の不溶性異物は、酸性結露水が筒状塩基性
物質の内管部より外管部へと流れるようにするた
めに設けた処理槽と筒状塩基性物質との隙間に堆
積するため、隙間を充分に確保することにより流
路の目詰まりは起こりにくくなる。
In order to achieve this object, the present invention arranges a cylindrical basic substance with a gap in a processing tank having a dam, guides acidic condensed water to the inner pipe part of the basic substance, and A flow of acidic condensation water is formed in which the acidic condensation water flows into the outer tube and comes into contact with the basic substance, and then overflows from the dam of the treatment tank. With this configuration, acidic dew condensation water comes into contact with the inner tube portion, outer tube portion, and bottom portion of the cylindrical basic substance, reacts, and is constantly neutralized before being discharged. On the other hand, the inner and outer tubes of the cylindrical basic substance react with acidic condensed water and dissolve, but the inner diameter of the inner tube increases as it dissolves, and the outer diameter of the outer tube increases as it dissolves. decreases, so there is little change in the contact area with acidic condensed water, and there is little decrease in neutralization ability due to dissolution of basic substances. Additionally, insoluble foreign substances such as corrosion products of heat exchangers and dust in the air are removed by a treatment tank installed to allow acidic condensation water to flow from the inner tube of the cylindrical basic substance to the outer tube. Since it is deposited in the gap between the cylindrical basic substance and the cylindrical basic substance, clogging of the channel becomes less likely to occur by ensuring a sufficient gap.

以下、本発明の実施例を第2図、第3図、第4
図を用いて説明する。
Embodiments of the present invention will be described below with reference to FIGS. 2, 3, and 4.
This will be explained using figures.

処理槽7内に配置した筒状塩基性物質8の内管
部9に酸性結露水が導かれるように流れが形成さ
れている。一方、処理槽7と筒状塩基性物質8と
に隙間を設けるために、処理槽7の大きさを筒状
塩基性物質8の大きさよりも大とし、かつ処理槽
7の底部に設けた突起10により筒状塩基性物質
8を処理槽7より浮いた状態にした。これによ
り、酸性結露水は筒状塩基性物質8の内管部9a
より外管部9bへと流れる。さらに、処理槽7に
は堰堤11が設けられ、堰堤11の高さを筒状塩
基性物質8の底面部の高さより高くしたため、酸
性結露水は筒状塩基性物質8と接触したのち堰堤
11より溢れて流出する。このような流れにより
酸性結露水は筒状塩基性物質8と接触して反応
し、中和処理されて排水される。
A flow is formed so that acidic dew condensation water is guided to the inner tube portion 9 of the cylindrical basic substance 8 placed in the treatment tank 7 . On the other hand, in order to provide a gap between the processing tank 7 and the cylindrical basic substance 8, the size of the processing tank 7 is made larger than the size of the cylindrical basic substance 8, and a protrusion is provided at the bottom of the processing tank 7. 10, the cylindrical basic substance 8 was made to float above the treatment tank 7. As a result, the acidic condensation water is removed from the inner tube portion 9a of the cylindrical basic substance 8.
It flows further toward the outer tube portion 9b. Further, the treatment tank 7 is provided with a dam 11, and the height of the dam 11 is made higher than the height of the bottom of the cylindrical basic material 8. It overflows and flows out more. Due to this flow, the acidic dew condensation water comes into contact with the cylindrical basic substance 8 and reacts with it, and is neutralized and drained.

筒状塩基性物質8を設置した処理槽7はボデイ
ー12に3個設けられ、処理槽7の前流には沈殿
槽13が設けられている。入口14より流入した
酸性結露水は、沈殿槽13へ導かれ、熱交換器の
腐食生成物や空気中の塵埃等の不溶性異物を沈殿
させる。沈殿槽より溢れて酸性結露水は案内溝1
5(第3図参照)を経由して自然落下し、処理槽
7内に設置した筒状塩基性物質8の内管部9aへ
滴下する。内管部9aより処理槽7に流入した酸
性結露水は、堰堤11の高さになるまで滞留し、
筒状塩基性物質8の内管部9aより外管部9bへ
と流れを形成して反応したのち、堰堤11より溢
れて流出し、次の処理槽に配置した筒状塩基性物
質の内管部へ滴下する。以下、この繰り返しによ
つて酸性結露水は筒状塩基性物質と接触して反応
し、中和処理され出口16より排出される。
Three processing tanks 7 in which cylindrical basic substances 8 are installed are provided in the body 12, and a sedimentation tank 13 is provided upstream of the processing tank 7. The acidic condensed water flowing in from the inlet 14 is led to the precipitation tank 13, where it precipitates insoluble foreign matter such as corrosion products of the heat exchanger and dust in the air. Acidic condensation water overflowing from the sedimentation tank flows into guide groove 1.
5 (see FIG. 3), and drops into the inner pipe portion 9a of the cylindrical basic substance 8 installed in the processing tank 7. The acidic condensed water that flows into the treatment tank 7 from the inner pipe part 9a stays until it reaches the height of the dam 11.
After forming a flow from the inner tube part 9a of the cylindrical basic substance 8 to the outer tube part 9b and reacting, it overflows from the dam 11 and flows out, and the inner tube of the cylindrical basic substance placed in the next processing tank drip onto the area. Thereafter, by repeating this process, the acidic condensed water comes into contact with the cylindrical basic substance, reacts, is neutralized, and is discharged from the outlet 16.

沈殿槽13と複数の処理槽は垂直方向に千鳥状
並んでおり、その配置を、槽より溢れた酸性結露
水が次の処理槽内に配置した筒状塩基性物質の内
管部に導かれるようにしている。また、バイパス
流路17を設け、沈殿槽13と処理槽7との間の
通路や処理槽間の通路が目詰まりした場合でも酸
性結露水が流れるようにするため、互に連通させ
その上部に排孔18を設けた。排孔18は出口1
6が目詰まりをした場合の通路である。
The sedimentation tank 13 and a plurality of treatment tanks are arranged in a staggered manner in the vertical direction, and the arrangement is such that the acidic condensation water overflowing from the tank is guided to the inner tube of a cylindrical basic substance placed in the next treatment tank. That's what I do. In addition, a bypass channel 17 is provided to allow acidic condensation water to flow even if the passage between the sedimentation tank 13 and the treatment tank 7 or the passage between the treatment tanks becomes clogged. A drainage hole 18 was provided. Exhaust hole 18 is outlet 1
6 is the passage in case of clogging.

上記構成にすることにより、(1)酸性結露水は確
実に塩基性物質と接触し常に一定の酸性度の処理
水を排出する。(2)筒状塩基性物質が溶解するとそ
の管外径は減少するが管内径は増加するため、酸
性結露水との接触面積の変化が少なく、中和能力
の低下が少なくなるとともに余分な塩基性物質を
準備する必要がなくなり、中和処理機構も小型に
なる。(3)筒状塩基性物質を突起により処理槽より
浮かした状態とし、かつ処理槽の大きさを簡状塩
基性物質の大きさより大として両者の間に隙間を
設けて酸性結露水が筒状塩基性物質の内管部より
外管部へ流れるようにしているため、熱交換器の
腐食生成物や空気中の塵埃等の不溶性異物は処理
槽の底に堆積し、流路の目詰まりが起こりにく
い。なお、実施例では沈殿槽を設けて、不溶性異
物による目詰り防止を確実にしている。
With the above configuration, (1) the acidic condensed water reliably comes into contact with the basic substance, and treated water with a constant acidity is always discharged. (2) When a cylindrical basic substance dissolves, its outer diameter decreases but its inner diameter increases, so there is little change in the contact area with acidic condensation water, less reduction in neutralization ability, and less excess base. There is no need to prepare a chemical substance, and the neutralization processing mechanism can also be made smaller. (3) The cylindrical basic substance is suspended from the processing tank by the protrusion, and the size of the processing tank is larger than the size of the simple basic substance, and a gap is provided between the two so that the acidic condensation water is formed into a cylindrical shape. Since the basic substance flows from the inner tube to the outer tube, insoluble foreign matter such as corrosion products of the heat exchanger and dust in the air will accumulate at the bottom of the treatment tank, preventing clogging of the flow path. Hard to happen. In the example, a settling tank is provided to ensure prevention of clogging due to insoluble foreign matter.

一方、塩基性物質は、Mg、Al等の金属やNa、
K、Li、Mg、Ca等の酸化物、炭酸塩、水酸化物
であり、これらは単一成分もしくは複数成分で用
いられる。
On the other hand, basic substances include metals such as Mg and Al, Na,
These are oxides, carbonates, and hydroxides of K, Li, Mg, Ca, etc., and these are used as a single component or multiple components.

本発明の効果を、Mgを用いた中和処理機構で
判定した。
The effects of the present invention were evaluated using a neutralization treatment mechanism using Mg.

中和処理機構は、高さ123mm、幅38mm、厚さ32
mmのアクリル樹脂ケース(板厚3mm)の中に、処
理槽を1槽配置したものであり、この内に外径φ
20mm、内径12mm、高さ90mm、重さ31gの筒状マグ
ネシウム(Mg96%、Al3%、Zn1%)を配置し
た。筒状マグネシウムは、突起により処理槽の底
部より5mmの高さで浮いた状態にあり、処理槽と
筒状マグネシウムとの隙間が最大7mmとなるよう
に両者の間に隙間を設けて長方体の処理槽に配置
した。
The neutralization mechanism has a height of 123 mm, a width of 38 mm, and a thickness of 32 mm.
One processing tank is placed inside an acrylic resin case (thickness: 3 mm) with an outer diameter of φ
A cylindrical magnesium tube (Mg96%, Al3%, Zn1%) with a diameter of 20 mm, an inner diameter of 12 mm, a height of 90 mm, and a weight of 31 g was placed. The cylindrical magnesium is suspended at a height of 5 mm from the bottom of the processing tank due to the protrusion, and a rectangular shape is created by providing a gap between the processing tank and the cylindrical magnesium so that the gap between the two is 7 mm at maximum. was placed in a treatment tank.

堰堤は、筒状マグネシウムの底面部より22mmの
高さにある。酸性結露水は、筒状マグネシウムの
内管部より流入し、内管部から外管部へと流れを
形成してマグネシウムと反応した後、堰堤より溢
れ外部へ排出される。
The dam is located at a height of 22 mm from the bottom of the magnesium cylinder. Acidic condensation water flows into the inner tube of the cylindrical magnesium tube, forms a flow from the inner tube to the outer tube, reacts with magnesium, and then overflows from the dam and is discharged to the outside.

この中和処理機構を、潜熱回収用熱交換器(表
面にスズメツキを施したもの)を有するガス湯沸
機に取付け、潜熱回収用熱交換器の表面に発生す
る酸性結露水を導いて中和処理を行なつた。酸性
結露水は、PH=3.0、水温30℃であり、60ml/hの
流量で中和処理機構へ流入していた。ガス湯沸機
を屋外で連続した結果を第5図に示す。酸性結露
水は長期間安定して中和処理され、酸度の高いま
ま排出されることはなかつた。また、Mgは3000
時間経過すると2.3g溶解していたが、その表面
積は目視による比較ではほとんど初期と同一であ
つた。さらに、熱交換器の腐食生成物や空気中の
塵埃等の不溶性異物が処理槽の底に堆積していた
が、これらの不溶性異物は流路の目詰まりを起こ
さなかつた。
This neutralization treatment mechanism is attached to a gas water heater that has a latent heat recovery heat exchanger (with tin plated surface), and the acidic condensation water generated on the surface of the latent heat recovery heat exchanger is guided and neutralized. I processed it. The acidic dew water had a pH of 3.0, a water temperature of 30°C, and was flowing into the neutralization treatment mechanism at a flow rate of 60ml/h. Figure 5 shows the results of continuous use of a gas water heater outdoors. The acidic condensed water was neutralized stably for a long period of time, and was not discharged with high acidity. Also, Mg is 3000
Although 2.3g had dissolved over time, the surface area was almost the same as the initial one when visually compared. Furthermore, although insoluble foreign substances such as corrosion products of the heat exchanger and dust in the air were deposited at the bottom of the processing tank, these insoluble foreign substances did not cause clogging of the flow path.

以上のように本発明の酸性結露水の中和処理機
構によれば次の効果が得られる。
As described above, according to the acidic dew water neutralization treatment mechanism of the present invention, the following effects can be obtained.

(1) 酸性結露水が、筒状塩基性物質の内管部より
流入して外管部へと流れて筒状塩基性物質と反
応したのち、処理槽の堰堤より溢れて流出して
いるため、確実に塩基性物質と反応して中和処
理され、酸度の高いまま排出されることがな
い。
(1) Acidic condensation water flows into the inner tube of the cylindrical basic material, flows to the outer tube, reacts with the cylindrical basic material, and then overflows from the dam of the treatment tank. , it is reliably neutralized by reacting with basic substances, and is not discharged with high acidity.

(2) 筒状塩基性物質であるため、酸性結露水と反
応して溶解する表面積の減少割合が少ないの
で、中和能力の低下が少ない。
(2) Since it is a cylindrical basic substance, the rate of decrease in surface area where it reacts and dissolves with acidic condensed water is small, so there is little decrease in neutralization ability.

(3) 筒状塩基性物質と処理槽との隙間を設け、酸
性結露水を筒状塩基性物質の内管部から外管部
へと流しているため、熱交換器の腐食生成物や
空気中の塵埃等の不溶性異物による流路の目詰
まりが起こりにくい。
(3) A gap is provided between the cylindrical basic material and the treatment tank, and acidic condensation water flows from the inner tube to the outer tube of the cylindrical basic material, so corrosion products from the heat exchanger and air The channel is less likely to be clogged by insoluble foreign matter such as dust inside.

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

第1図は従来の中和処理装置の正断面図、第2
図は本発明の一実施例における酸性結露水の中和
処理装置を示す正断面図、第3図は第2図のA―
A′線断面図、第4図は第2図B―B′線切欠斜視
図、第5図は本発明の装置の特性図である。 7……処理槽、8……筒状塩基性物質、9a…
…内管部、9b……外管部、11……堰堤。
Figure 1 is a front cross-sectional view of a conventional neutralization treatment device;
The figure is a front sectional view showing a neutralization treatment device for acidic condensed water according to an embodiment of the present invention, and FIG.
4 is a sectional view taken along the line A', FIG. 4 is a cutaway perspective view taken along the line B--B' in FIG. 2, and FIG. 5 is a characteristic diagram of the device of the present invention. 7... Processing tank, 8... Cylindrical basic substance, 9a...
...Inner pipe part, 9b...Outer pipe part, 11...Weir.

Claims (1)

【特許請求の範囲】[Claims] 1 筒状塩基性物質を堰堤を有する処理槽内に隙
間を設けて配置し、酸性結露水を上記筒状塩基性
物質の内管部から外管部へと流し堰堤から溢れて
流出させる酸性結露水の中和処理装置。
1 Acidic condensation in which a cylindrical basic substance is placed with a gap in a treatment tank having a dam, and acidic condensation water flows from the inner pipe part of the cylindrical basic material to the outer pipe part and overflows from the dam. Water neutralization treatment equipment.
JP57006297A 1982-01-18 1982-01-18 Neutralization equipment for acidic condensed water Granted JPS58122086A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57006297A JPS58122086A (en) 1982-01-18 1982-01-18 Neutralization equipment for acidic condensed water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57006297A JPS58122086A (en) 1982-01-18 1982-01-18 Neutralization equipment for acidic condensed water

Publications (2)

Publication Number Publication Date
JPS58122086A JPS58122086A (en) 1983-07-20
JPS6220875B2 true JPS6220875B2 (en) 1987-05-09

Family

ID=11634433

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57006297A Granted JPS58122086A (en) 1982-01-18 1982-01-18 Neutralization equipment for acidic condensed water

Country Status (1)

Country Link
JP (1) JPS58122086A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10309587A (en) * 1997-05-12 1998-11-24 Rinnai Corp Neutralizing agent and neutralizing device
GB2464660A (en) * 2008-08-13 2010-04-28 Alpha Fry Ltd Device for chemically treating condensate from a domestic boiler
JP2013150942A (en) * 2012-01-24 2013-08-08 Corona Corp Neutralization device and water heater having the same
JP5868773B2 (en) * 2012-05-08 2016-02-24 株式会社コロナ Neutralizer and hot water supply apparatus having the same

Also Published As

Publication number Publication date
JPS58122086A (en) 1983-07-20

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