JP3008976B2 - Organic waste liquid incinerator - Google Patents

Organic waste liquid incinerator

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Publication number
JP3008976B2
JP3008976B2 JP10052321A JP5232198A JP3008976B2 JP 3008976 B2 JP3008976 B2 JP 3008976B2 JP 10052321 A JP10052321 A JP 10052321A JP 5232198 A JP5232198 A JP 5232198A JP 3008976 B2 JP3008976 B2 JP 3008976B2
Authority
JP
Japan
Prior art keywords
space
incinerator
organic waste
waste liquid
partition member
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 - Fee Related
Application number
JP10052321A
Other languages
Japanese (ja)
Other versions
JPH10253034A (en
Inventor
幸之輔 中村
泰男 木本
郁子 中村
Original Assignee
株式会社ジーテック
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
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Priority to JP10052321A priority Critical patent/JP3008976B2/en
Publication of JPH10253034A publication Critical patent/JPH10253034A/en
Application granted granted Critical
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Anticipated expiration legal-status Critical
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Links

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、有機廃液の焼却炉
に関する。
The present invention relates to an organic waste liquid incinerator.

【0002】[0002]

【従来の技術】有機廃液を乾燥焼却する際の排気ガスの
クリーン化を図るため、例えば白金触媒による低温脱臭
が試みられている。
2. Description of the Related Art Attempts at low-temperature deodorization using, for example, a platinum catalyst have been attempted in order to clean exhaust gas when drying and burning organic waste liquid.

【0003】[0003]

【発明が解決しようとする課題】しかし、この方法は、
維持費や設備費が大であるために広く普及するには至っ
ていない。
However, this method is
Due to the high maintenance and equipment costs, it has not been widely used.

【0004】一方、焼却炉での乾燥焼却中には、焼却温
度の管理が重要となる。すなわち、燃焼温度が高すぎる
と、過酸化物が生じたり、化学重合による変成により N
Ox等の有害分解ガスが発生するおそれがある。
On the other hand, during dry incineration in an incinerator, management of the incineration temperature is important. That is, if the combustion temperature is too high, peroxides are generated or N
Hazardous decomposition gas such as Ox may be generated.

【0005】そこで、本発明は、有機物を含む廃液を、
有害ガスを生成することなく確実に焼却処分することの
できる焼却炉の提供を目的とする。
[0005] Therefore, the present invention provides a waste liquid containing organic matter,
It is an object of the present invention to provide an incinerator that can be surely incinerated without generating harmful gas.

【0006】[0006]

【課題を解決するための手段】上記目的を達成すべく、
本発明にかかる有機廃液の焼却炉は、炉体内に、上下に
離隔させて2枚の通気性を有する仕切り部材を配置する
ことにより、炉体内を、下段の仕切り部材よりも下方の
燃焼空間と、両仕切り部材に挟まれた蒸発空間と、上段
の仕切り部材よりも上方の脱臭空間とに区画形成し、燃
焼空間及び脱臭空間にバーナーを配置すると共に、蒸発
空間に有機廃液を噴霧するノズルを配置したものであ
る。
In order to achieve the above object,
The organic waste liquid incinerator according to the present invention has a structure in which two air-permeable partition members are vertically separated from each other in the furnace body, so that the inside of the furnace is in a combustion space below the lower partition member. A partition for forming an evaporation space between the two partition members and a deodorizing space above the upper partition member, a burner disposed in the combustion space and the deodorizing space, and a nozzle for spraying organic waste liquid into the evaporation space. It is arranged.

【0007】仕切り部材は、複数段に積層した金網で構
成するのがよい。
[0007] The partition member is preferably composed of a wire mesh laminated in a plurality of stages.

【0008】[0008]

【発明の実施の形態】以下、本発明の実施形態を図1乃
至図4に基いて説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to FIGS.

【0009】図1に示すように、本発明にかかる焼却炉
(87)は、有底筒状をなす炉体(90)と、炉体(90)内
に上下二段に離隔して設けた仕切り部材(91a)(91
b)と、両仕切り部材(91a)(91b)の間の空間(9
7:蒸発空間)に下向きに配置された複数個のノズル(9
2)と、下段の仕切り部材(91a)よりも下方の空間(9
6:燃焼空間)、及び、上段の仕切り部材(91b)より
も上方の空間(99:脱臭空間)にそれぞれ配置されたバ
ーナー(93a)(93b)と、炉体(90)の上部に取り付
けた煙突(94)とで構成される。
As shown in FIG. 1, an incinerator (87) according to the present invention is provided in a furnace body (90) having a cylindrical shape with a bottom, and is provided in the furnace body (90) so as to be vertically separated from each other. Partition member (91a) (91
b) and the space (9) between the partition members (91a) and (91b).
7: A plurality of nozzles (9
2) and the space (9) below the lower partition member (91a).
6: combustion space), and burners (93a) (93b) arranged in a space (99: deodorizing space) above the upper partition member (91b), and were attached to the upper part of the furnace body (90). Consists of a chimney (94).

【0010】両仕切り部材(91a)(91b)は、図2に
示すように、複数枚(70〜80枚程度)の金網(107 )を
メッシュを適当に交差させつつ積層して構成され、格子
状の支持材(95)の上に隙間なく並べられている。
As shown in FIG. 2, both partition members (91a) and (91b) are formed by laminating a plurality of (about 70 to 80) wire meshes (107) while appropriately intersecting meshes. Are arranged without gaps on the support material (95).

【0011】両バーナー(93a)(93b)は、炉体(9
0)内で燃焼ガスの旋回流を形成できるよう、炉体(9
0)の接線方向に向けて配置されている(図3参照)。
The two burners (93a) and (93b) are connected to the furnace body (9).
(0) so that a swirling flow of combustion gas can be formed inside
0) (see FIG. 3).

【0012】炉体(90)は、熱効率を高めるべく、中間
部に空気層を有する二重構造とされている。
The furnace body (90) has a double structure having an air layer at an intermediate portion in order to increase thermal efficiency.

【0013】下段の仕切り部材(91a)よりも下方の燃
焼空間(96)は、下段のバーナー(93a)により500
℃前後に加熱される。また、両仕切り部材(91a)(91
b)間の蒸発空間(97)は、上下の仕切り部材(91a)
(91b)からの伝熱及びこれらを通過した燃焼ガスによ
り200℃程度に加熱される。
The combustion space (96) below the lower partitioning member (91a) is provided with a lower burner (93a).
Heated to around ° C. Further, both partition members (91a) (91
The evaporating space (97) between b) and the upper and lower partition members (91a)
It is heated to about 200 ° C. by the heat transfer from (91b) and the combustion gas passing therethrough.

【0014】有機廃水は各ノズル(92)に供給され、ノ
ズル(92)から蒸発空間(96)に噴霧される。噴霧され
た有機廃水の多くは、噴霧された直後に蒸発空間(97)
内で蒸発するが、蒸発しきれなかった有機廃水は、下段
の仕切り部材(91a)の上に落下する。落下した有機廃
水は、下段の仕切り部材(91a)の有効接触面積が27
0〜370m2/m3にも達するため、当該仕切り部材(91
a)から下方に滴下することなくこれに保持されて完全
に蒸発する。一方、有機廃水中の有機固形分も同様に、
蒸発空間(97)内及び下段の仕切り部材(91a)の表層
近傍で燃焼する。このように有機廃水の多くは、比較的
低温(200℃前後)の雰囲気下で高温に曝されること
なく蒸発、燃焼するため、過酸化物の発生や化学重合に
よる変性を招くこともない。一般に、NOx 等の有害ガス
は600℃を越えるような高温燃焼時に生成され、上記
低温条件下ではほとんど生じない。
The organic wastewater is supplied to each nozzle (92) and is sprayed from the nozzle (92) into the evaporation space (96). Most of the sprayed organic wastewater evaporates immediately after being sprayed (97)
The organic wastewater that evaporates inside but does not evaporate falls onto the lower partition member (91a). The falling organic wastewater has an effective contact area of 27% for the lower partition member (91a).
0 to 370 m 2 / m 3 , the partition member (91
It is retained by this without dripping downward from a) and evaporates completely. On the other hand, organic solids in organic wastewater are
It burns in the evaporation space (97) and near the surface of the lower partition member (91a). As described above, most of the organic wastewater evaporates and burns in a relatively low-temperature (around 200 ° C.) atmosphere without being exposed to a high temperature, and thus does not cause generation of peroxides or modification due to chemical polymerization. Generally, harmful gases such as NOx are generated during high-temperature combustion exceeding 600 ° C., and hardly occur under the above-mentioned low-temperature conditions.

【0015】低温ガスとの接触によって、蒸発した有機
廃水は、上段の積層金網(91b)で加熱され、当該金網
(91b)よりも上方の脱臭空間(99)で上段のバーナー
(93b)によって適当な温度(例えば500℃程度)ま
で昇温される。これにより、下方で発生した煙や臭気物
質が燃焼するので、煙突(94)から排出される排ガス
は、無煙無臭となる。上段の仕切り部材(91b)は、燃
焼ガスの整流効果をも発揮するので、脱臭空間(99)内
での不均一昇温を防止して排ガスの無煙無臭化に大きく
貢献する。また、当該仕切り部材(91b)は、蒸発空間
(97)内で浮遊する有機物の燃えかすが脱臭空間(99)
へ侵入するのを防止するフィルタとしての役割も果た
す。
The organic wastewater evaporated by the contact with the low-temperature gas is heated by the upper layered wire mesh (91b), and is appropriately heated by the upper burner (93b) in the deodorizing space (99) above the wire mesh (91b). Temperature (for example, about 500 ° C.). As a result, smoke and odorous substances generated below are burned, and the exhaust gas discharged from the chimney (94) is smokeless and odorless. Since the upper partition member (91b) also exerts a rectifying effect on the combustion gas, it prevents uneven heating in the deodorizing space (99) and greatly contributes to smokeless and odorless exhaust gas. In addition, the partition member (91b) is used to remove the organic matter flammable in the evaporation space (97) but the deodorant space (99).
Also acts as a filter to prevent intrusion into the system.

【0016】フード(100 )内には、天蓋(101 )が設
置されており、この天蓋(101 )により高温ガスの素通
りや短絡(ショートパス)を防止して無煙無臭の排ガス
を放出することが可能となる。燃焼後の灰分は、下段の
積層金網(91a)を通って炉体(90)の床板(102 )上
に堆積し、炉体(90)に設けたマンホール(103 )から
定期的に排出される。このマンホール(103 )は炉内の
点検窓としての役割も果たす。
In the hood (100), a canopy (101) is installed. The canopy (101) prevents hot gas from passing through or short-circuiting (short path) to discharge smokeless and odorless exhaust gas. It becomes possible. The ash after combustion passes through the lower laminated wire mesh (91a) and accumulates on the floor plate (102) of the furnace body (90), and is periodically discharged from manholes (103) provided in the furnace body (90). . This manhole (103) also serves as an inspection window in the furnace.

【0017】(104a)(104b)は、両バーナー(93a)
(93b)の出力を制御するための制御器であり、それぞ
れセンサ(105a)(105b)によって炉内温度を検知し、
逐次バーナー(93a)(93b)を制御して各空間(96)
(97)(99)を所定温度に保持する。また、(106 )
は、排ガス放出を制御するダンパーであり、炉内圧を調
整して外気の侵入や燃焼ガスの炉内における偏流を防止
する。仕切り部材(91a)(91b)としては、空間を断
熱的に仕切ることができ、しかもある程度の通気性を有
する限り積層金網以外の他の部材(多孔板等)を使用し
てもよい。
(104a) and (104b) are both burners (93a)
(93b) is a controller for controlling the output, the temperature in the furnace is detected by the sensor (105a) (105b), respectively,
By controlling the sequential burners (93a) and (93b), each space (96)
(97) Hold (99) at a predetermined temperature. Also, (106)
Is a damper for controlling the emission of exhaust gas, and adjusts the furnace pressure to prevent intrusion of outside air and drift of combustion gas in the furnace. As the partition members (91a) and (91b), other members (such as a perforated plate) other than the laminated wire mesh may be used as long as they can partition the space insulatively and have a certain degree of air permeability.

【0018】この焼却炉(87)は、有機物の遠心分離、
例えば煎茶等の抽出液から煎茶の微量固形分を除去する
工程において、遠心分離機の洗浄排水を焼却乾燥する場
合に適用することができる。図4に、このような工程の
システム図を示す。
[0018] The incinerator (87) is used for centrifugal separation of organic matter,
For example, in the step of removing trace solids of sencha from an extract such as sencha, the present invention can be applied to the case where the washing wastewater from a centrifuge is incinerated and dried. FIG. 4 shows a system diagram of such a process.

【0019】図4において、抽出エキス受槽(80)に貯
留された抽出エキスは、供給ポンプ(81)を介して抽出
エキス供給ヘッドタンク(82)に供給される。ヘッドタ
ンク(82)からの抽出液は、遠心分離機(1)にて遠心
分離され、抽出液中の微量固形分が遠心分離機(1)の
回転ボウルの内壁面に捕集され、クリアエキスのみが排
液口(5)から排出されて製品化される。
In FIG. 4, the extracted extract stored in the extracted extract receiving tank (80) is supplied to an extracted extract supply head tank (82) via a supply pump (81). The extract from the head tank (82) is centrifuged by the centrifuge (1), and a minute amount of solids in the extract is collected on the inner wall of the rotating bowl of the centrifuge (1), and the clear extract is collected. Only the product is discharged from the drain port (5) and commercialized.

【0020】回転ボウルの内壁に堆積した固形粒子分の
堆積層が増加して通液不能になると、洗浄装置(7)が
作動し、回転ボウル内に、洗浄水供給タンク(83)から
圧送された高圧洗浄水を噴射してボウル内壁面に付着し
た微量固形分を洗い流す。この洗浄排水は、排出口から
機外に排出され、排出管(84)を介して洗浄排水受槽
(85)に貯留される。洗浄排水受槽(85)の洗浄排水は
ポンプ(86)によって上述の焼却炉(87)のノズル(9
2)に供給され、この焼却炉(87)内で有機固形分を含
む洗浄排水が乾燥焼却される。なお、(88)は、各配管
の弁やポンプ、及び、焼却炉(87)のバーナー(93a)
(93b)等を制御するための制御盤である。
When the amount of solid particles deposited on the inner wall of the rotating bowl increases and the liquid cannot pass therethrough, the washing device (7) is operated, and the washing water is fed from the washing water supply tank (83) into the rotating bowl. High-pressure washing water is sprayed to wash off trace solids attached to the inner wall surface of the bowl. The washing wastewater is discharged from the outlet through the discharge port, and is stored in the washing wastewater receiving tank (85) via the discharge pipe (84). The washing wastewater from the washing wastewater receiving tank (85) is supplied to the nozzle (9) of the incinerator (87) by the pump (86).
The wastewater is supplied to 2) and the washing wastewater containing organic solids is dried and incinerated in the incinerator (87). (88) is a valve and pump for each pipe, and a burner (93a) of the incinerator (87).
(93b) A control panel for controlling the like.

【0021】[0021]

【発明の効果】本発明にかかる焼却炉によれば、廃液中
の有機微量固形分を確実に乾燥燃焼することができ、こ
れらが外気に排出されることもないので、微量固形分に
よる環境破壊を招くことはない。また、低温条件下で液
体を蒸発させた後、蒸発ガスを昇温して消臭等する構造
であるから、高温条件下で一気に蒸発燃焼させる場合の
ように、過酸化物や活性基酸化物等が生成されることも
なく、クリーンで無公害の排気ガスとすることができ、
環境保全に対する貢献度も大である。
According to the incinerator according to the present invention, the organic trace solids in the waste liquid can be surely dried and burned, and they are not discharged to the outside air. Will not be invited. In addition, since the liquid is evaporated under low-temperature conditions, the temperature of the evaporating gas is raised to deodorize, etc. Etc. are not generated, and clean and pollution-free exhaust gas can be obtained.
The contribution to environmental conservation is also large.

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

【図1】本発明にかかる焼却炉の垂直断面図である。FIG. 1 is a vertical sectional view of an incinerator according to the present invention.

【図2】積層金網の斜視図である。FIG. 2 is a perspective view of a laminated wire mesh.

【図3】焼却炉の平面図である。FIG. 3 is a plan view of the incinerator.

【図4】上記焼却炉を用いたシステム構成例を示す図で
ある。
FIG. 4 is a diagram showing an example of a system configuration using the incinerator.

【符号の説明】[Explanation of symbols]

90 炉体 91a 仕切り部材 91b 仕切り部材 92 ノズル 93a バーナー 93b バーナー 96 燃焼空間 97 蒸発空間 99 脱臭空間 90 Furnace body 91a Partition member 91b Partition member 92 Nozzle 93a Burner 93b Burner 96 Combustion space 97 Evaporation space 99 Deodorization space

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭62−175510(JP,A) 特開 昭62−91713(JP,A) (58)調査した分野(Int.Cl.7,DB名) F23G 7/04 601 F23G 7/04 602 F23G 7/04 ZAB ────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-62-175510 (JP, A) JP-A-62-91713 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) F23G 7/04 601 F23G 7/04 602 F23G 7/04 ZAB

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 炉体内に、上下に離隔させて2枚の通気
性を有する仕切り部材を配置することにより、炉体内
を、下段の仕切り部材よりも下方の燃焼空間と、両仕切
り部材に挟まれた蒸発空間と、上段の仕切り部材よりも
上方の脱臭空間とに区画形成し、燃焼空間及び脱臭空間
にバーナーを配置すると共に、蒸発空間に有機廃液を噴
霧するノズルを配置したことを特徴とする有機廃液の焼
却炉。
1. A furnace in which two air-permeable partitioning members are vertically spaced apart from each other, so that the furnace is sandwiched between a combustion space below a lower partitioning member and both partitioning members. And a deodorizing space above the upper partition member, a burner is disposed in the combustion space and the deodorizing space, and a nozzle for spraying organic waste liquid is disposed in the evaporating space. Organic waste incinerator.
【請求項2】 前記仕切り部材が複数段に積層した金網
からなることを特徴とする請求項1記載の有機廃液の焼
却炉。
2. The incinerator for organic waste liquid according to claim 1, wherein said partition member comprises a wire mesh laminated in a plurality of stages.
JP10052321A 1998-03-04 1998-03-04 Organic waste liquid incinerator Expired - Fee Related JP3008976B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10052321A JP3008976B2 (en) 1998-03-04 1998-03-04 Organic waste liquid incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10052321A JP3008976B2 (en) 1998-03-04 1998-03-04 Organic waste liquid incinerator

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP9700996A Division JP2816133B2 (en) 1996-04-18 1996-04-18 Centrifuge and regeneration system for polishing liquid and the like using the same

Publications (2)

Publication Number Publication Date
JPH10253034A JPH10253034A (en) 1998-09-25
JP3008976B2 true JP3008976B2 (en) 2000-02-14

Family

ID=12911540

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10052321A Expired - Fee Related JP3008976B2 (en) 1998-03-04 1998-03-04 Organic waste liquid incinerator

Country Status (1)

Country Link
JP (1) JP3008976B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4854889B2 (en) * 2001-09-21 2012-01-18 株式会社レボインターナショナル Method for producing diesel fuel oil from waste cooking oil
AU2002348596A1 (en) * 2002-10-28 2004-05-13 Po And Co Inc Waste burning apparatus for constraint ventilation form
CN101825285B (en) * 2010-05-17 2012-08-08 北京航天动力研究所 Burning treatment method and device for organic waste water containing salt
CN110160064B (en) * 2019-06-17 2021-01-15 江西楚杭环保科技有限公司 High-concentration organic industrial wastewater treatment equipment and purification treatment method thereof

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Publication number Publication date
JPH10253034A (en) 1998-09-25

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