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JPH0245519B2 - - Google Patents
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JPH0245519B2 - - Google Patents

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Publication number
JPH0245519B2
JPH0245519B2 JP58190629A JP19062983A JPH0245519B2 JP H0245519 B2 JPH0245519 B2 JP H0245519B2 JP 58190629 A JP58190629 A JP 58190629A JP 19062983 A JP19062983 A JP 19062983A JP H0245519 B2 JPH0245519 B2 JP H0245519B2
Authority
JP
Japan
Prior art keywords
drying
air
heat
blower
drying chamber
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 - Lifetime
Application number
JP58190629A
Other languages
Japanese (ja)
Other versions
JPS6082775A (en
Inventor
Katsuyuki Kataoka
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.)
Ebara Corp
Original Assignee
Ebara Infilco 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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP58190629A priority Critical patent/JPS6082775A/en
Publication of JPS6082775A publication Critical patent/JPS6082775A/en
Publication of JPH0245519B2 publication Critical patent/JPH0245519B2/ja
Granted legal-status Critical Current

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  • Drying Of Solid Materials (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、下水、し尿、各種産業廃水等の有機
性汚水処理において発生する含水物の省エネルギ
的な乾燥方法に関し、特に含水物の乾燥工程と有
機性汚水及び又は有機性汚泥の曝気工程の両者が
併存する場合に有効に適用しうる乾燥方法に関す
るものである。
Detailed Description of the Invention [Field of Industrial Application] The present invention relates to an energy-saving method for drying water-containing materials generated in the treatment of organic sewage such as sewage, human waste, and various industrial wastewater, and in particular to a method for drying water-containing materials. The present invention relates to a drying method that can be effectively applied when both a process and an aeration process of organic sewage and/or organic sludge coexist.

〔従来の技術〕[Conventional technology]

従来、含水物を乾燥するには、一般に重油、灯
油、ガスなどの燃料又は電気を多量に必要とし、
きわめてエネルギーを消費する方法がとられてい
た。
Conventionally, drying hydrated materials generally requires a large amount of fuel such as heavy oil, kerosene, gas, or electricity.
This method was extremely energy consuming.

また、下水、し尿、各種産業廃水等の有機性汚
水処理においては、生物処理や有機性汚泥の好気
性消化などに空気を供給することを目的としてブ
ロワが設置されていた。
Furthermore, in the treatment of organic wastewater such as sewage, human waste, and various industrial wastewater, blowers have been installed for the purpose of supplying air for biological treatment and aerobic digestion of organic sludge.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

そして、これらブロワは単に空気を供給すると
いつた単一の機能しか発揮されていないが、この
ことは何ら疑問をもたれておらず、これらブロワ
に複合的機能を付与するという技術思想は全くみ
られなかつた。
Although these blowers only perform a single function, such as simply supplying air, there is no question about this, and there is no technical idea to give these blowers multiple functions. Nakatsuta.

本発明は、このように従来全く顧みられなかつ
たブロワのエネルギーに着目して完成されたもの
である。すなわち、ブロワは空気圧縮機であるか
ら、熱力学における気体の断熱圧縮理論に示され
るように、ブロワ吐出空気の温度は吸込空気の温
度よりもかなり上昇し、大気温度が10〜20℃の場
合、ブロワ吐出空気の温度は80〜100℃にも達す
ることに着目して本発明が完成されたものであ
る。
The present invention was completed by focusing on the energy of the blower, which has not been considered at all in the past. In other words, since the blower is an air compressor, as shown in the adiabatic compression theory of gases in thermodynamics, the temperature of the blower discharge air will be much higher than the temperature of the suction air, and when the atmospheric temperature is 10 to 20 degrees Celsius. The present invention was developed by focusing on the fact that the temperature of blower discharge air reaches as high as 80 to 100°C.

本発明は、ブロワ吐出空気の保有熱を巧みに回
収、有効利用し、含水物を燃料を全く必要とせず
に乾燥することができる省エネルギ的な乾燥方法
を提供することを目的とするものである 〔課題を解決するための手段〕 本発明は、有機性汚水処理において発生する含
水物を乾燥する乾燥室を密閉構造とし、該乾燥室
内の空気をブロワにて吸引し、該ブロワ吐出空気
の保有熱によつて空気を加温し、得られた温風を
前記ブロワの吸気によつて前記乾燥室内に吸引し
て乾燥用熱源として利用し、その降温したブロワ
吐出空気をヒートポンプの冷媒蒸発部に接触させ
て冷却、除湿するとともに該ヒートポンプの冷媒
凝縮部からの放熱を前記乾燥室における乾燥用熱
源として利用し、さらに前記ヒートポンプの冷媒
蒸発部から流出する低温低湿のブロワ吐出空気を
有機性汚水及び又は有機性汚泥の曝気工程にて利
用することを特徴とする含水物の乾燥方法であ
る。
An object of the present invention is to provide an energy-saving drying method that skillfully recovers and effectively utilizes the heat retained in blower discharge air and can dry water-containing materials without requiring any fuel. [Means for Solving the Problems] The present invention has a drying chamber for drying water-containing substances generated in organic wastewater treatment, which has a sealed structure, and the air inside the drying chamber is sucked by a blower, and the air discharged from the blower is The air is heated by the retained heat, and the resulting warm air is drawn into the drying chamber by the intake air of the blower and used as a heat source for drying, and the cooled blower discharge air is transferred to the refrigerant evaporation section of the heat pump At the same time, the heat released from the refrigerant condensing section of the heat pump is used as a heat source for drying in the drying chamber, and the low-temperature, low-humidity blower discharge air flowing out from the refrigerant evaporating section of the heat pump is used to cool and dehumidify organic wastewater. This is a method for drying a water-containing material, characterized in that it is used in an aeration process of organic sludge and/or organic sludge.

〔実施例〕〔Example〕

本発明の一実施例を、下水処理施設を例にとり
あげて、図面を参照しながら説明すれば次の通り
である。
An embodiment of the present invention will be described below with reference to the drawings, taking a sewage treatment facility as an example.

下水汚泥の脱水ケーキその他下水処理施設にお
いて発生した乾燥しようする含水固形物1を収納
した密閉構造の乾燥室2の壁Aは、断熱材にて外
気と遮断しており、乾燥室2内の空気3は曝気用
のブロワ4によつて吸引、圧縮されるが、この過
程で圧縮熱が発生し、ブロワ吐出空気5の温度は
80〜100℃程度に昇温する。このブロワ吐出空気
5の熱を回収するために、ブロワ吐出空気5を熱
交換器6に流入させて空気7を加温し、得られた
温風7′を乾燥室2内に導いて含水固形物1の乾
燥用熱源に利用する。
The wall A of the drying chamber 2, which has a closed structure and houses the dehydrated cake of sewage sludge and other water-containing solids 1 to be dried generated in sewage treatment facilities, is isolated from the outside air with a heat insulating material, and the air inside the drying chamber 2 is 3 is sucked and compressed by the aeration blower 4, but heat of compression is generated in this process, and the temperature of the blower discharge air 5 is
Raise the temperature to about 80-100℃. In order to recover the heat of this blower discharge air 5, the blower discharge air 5 is caused to flow into a heat exchanger 6 to heat the air 7, and the obtained warm air 7' is guided into the drying chamber 2 to dry the water-containing solids. Used as a heat source for drying item 1.

一方、熱交換器6によつて空気7を加温するこ
とにより、自身は降温したブロワ吐出空気には、
乾燥対象含水固形物1から蒸発した水蒸気が多量
に含まれており、高湿空気5′となつているため、
この水蒸気の保有する潜熱を回収して乾燥用熱源
に利用する。このために高湿空気5′をヒートポ
ンプのフロンなどの冷媒蒸発部8に接触させて冷
却し、水蒸気を擬縮させることにより凝縮潜熱を
回収し、発生した凝縮水はドレン9より排出させ
る。
On the other hand, by heating the air 7 with the heat exchanger 6, the blower discharge air, which itself has been cooled, has
Since it contains a large amount of water vapor evaporated from the water-containing solid material 1 to be dried and becomes high humidity air 5',
The latent heat possessed by this water vapor is recovered and used as a heat source for drying. For this purpose, the high-humidity air 5' is cooled by contacting with a refrigerant evaporator 8 such as a fluorocarbon of a heat pump, the latent heat of condensation is recovered by pseudo-condensing the water vapor, and the generated condensed water is discharged from a drain 9.

したがつて、ヒートポンプの冷媒凝縮部10
(放熱部)からは、高湿空気5′から回収した水蒸
気凝縮潜熱とヒートポンプの冷媒圧縮11にイン
プツトされた動力に相当する熱量(1kwH=
860Kcal)の合計量が放散されるから、この熱も
乾燥用熱源として利用する。
Therefore, the refrigerant condensing section 10 of the heat pump
(heat dissipation section), the latent heat of water vapor condensation recovered from the high-humidity air 5' and the amount of heat equivalent to the power input to the refrigerant compression 11 of the heat pump (1kwH =
Since the total amount of heat (860Kcal) is dissipated, this heat is also used as a heat source for drying.

なお、12は冷媒の膨張弁を示す。 Note that 12 indicates a refrigerant expansion valve.

また、ヒートポンプの冷媒蒸発部8(高湿空気
5′の冷媒除湿部)から流出する低温低湿空気
5″は未だ高い圧力を保有しており、下水の活性
汚泥処理のエアレーシヨンタンク13内の散気装
置14に供給したり、有機性汚泥の曝気に利用す
る。
In addition, the low-temperature, low-humidity air 5'' flowing out from the refrigerant evaporation section 8 (refrigerant dehumidification section of the high-humidity air 5') of the heat pump still has a high pressure, and is used in the aeration tank 13 for activated sludge treatment of sewage. It is supplied to the aeration device 14 or used for aeration of organic sludge.

なお、低温低湿空気5″を下水の活性汚泥処理
のエアレーシヨンタンク13に供給するので、特
別の脱臭工程が不要となる。すなわち、下水汚泥
の脱水ケーキなどの乾燥においては悪臭ガスが発
生するが、この乾燥排ガスはエアレーシヨンタン
ク13に供給されて曝気に利用される結果、エア
レーシヨンタンク13内に多量に生息する活性汚
泥微生物によつて生物学的に脱臭されるから、脱
臭設備、運転費などが不要になる。
In addition, since the low-temperature, low-humidity air 5'' is supplied to the aeration tank 13 for activated sludge treatment of sewage, a special deodorizing process is not required.In other words, foul-smelling gas is generated when drying a dehydrated cake of sewage sludge. However, as this dry exhaust gas is supplied to the aeration tank 13 and used for aeration, it is biologically deodorized by the activated sludge microorganisms living in the aeration tank 13 in large quantities. , operating costs become unnecessary.

なお、前述の本発明における乾燥用熱源に利用
したブロワ吐出空気としては、空気圧縮機等の吐
出空気も含まれるものである。
Note that the blower discharge air used as the drying heat source in the above-mentioned present invention also includes discharge air from an air compressor or the like.

さらにまた、本発明の他の実施態様について述
べれば次の通りである。
Furthermore, other embodiments of the present invention will be described as follows.

ブロワ4を乾燥室2内に設置すれば、ブロワ
4本体から発生する熱が乾燥室2内に放散さ
れ、乾燥に利用できる熱量が増加する。
When the blower 4 is installed in the drying chamber 2, the heat generated from the blower 4 body is dissipated into the drying chamber 2, increasing the amount of heat that can be used for drying.

ヒートポンプの冷媒凝縮部10は、乾燥室2
の内部に配備するも、あるいは熱交換器6にて
加湿された温風7′と直接熱交換するようにし
てもよい。
The refrigerant condensing section 10 of the heat pump has a drying chamber 2
Alternatively, the heat exchanger 6 may directly exchange heat with humidified warm air 7'.

乾燥室2としては、回分乾燥方式でも連続乾
燥方式でも採用することができる。
As the drying chamber 2, either a batch drying method or a continuous drying method can be employed.

〔発明の効果〕〔Effect of the invention〕

以上述べたように、本発明は、従来単に空気を
供給するといつた単一の機能しか発揮されていな
かつたブロワの吐出空気の保有熱を回収し、含水
物の乾燥に有効利用するものであるから、次のよ
うなきわめて重要な効果をうることができる。
As described above, the present invention recovers the heat retained in the air discharged from the blower, which conventionally only had a single function of simply supplying air, and effectively utilizes it for drying water-containing materials. The following very important effects can be obtained from this:

従来、重油などの燃料を必要としていた含水
物の乾燥にブロワ圧縮熱を利用するから、顕著
な省エネルギ効果があり、乾燥用燃料が不要に
なる。
Since blower compression heat is used to dry water-containing materials, which conventionally required fuel such as heavy oil, there is a significant energy-saving effect and no drying fuel is required.

含水物の乾燥で蒸発した水分の潜熱を回収
し、ブロワの圧縮熱とともに乾燥用熱源として
利用するようにしたので、さらに省エネルギ的
な乾燥が可能となる。
Since the latent heat of the water evaporated during drying of the hydrated material is recovered and used as a heat source for drying along with the compression heat of the blower, even more energy-saving drying is possible.

乾燥室は密閉構造であるから、温風はブロワ
の吸引力によつて、自動的に乾燥室内に流入す
るから、別個にフアンを設ける必要はない。
Since the drying chamber has a closed structure, hot air automatically flows into the drying chamber by the suction force of the blower, so there is no need to provide a separate fan.

含水物の乾燥を行つた結果として、圧力を保
有する低温、低湿の空気が自動的に得られるか
ら、この空気を有機性汚水、有機性汚泥のエア
レーシヨン用に利用できるので、エアレーシヨ
ン動力が不要となる。
As a result of drying water-containing materials, low-temperature, low-humidity air that retains pressure is automatically obtained, and this air can be used for aeration of organic wastewater and organic sludge, eliminating the need for aeration power. Become.

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

図面は本発明の一実施例を示す系統説明図であ
る。 1…含水固形物、2…乾燥室、3…空気、4…
ブロワ、5…ブロワ吐出空気、5′高湿空気、
5″…低温低湿空気、6…熱交換器、7…空気、
7′…温風、8…冷媒蒸発部、10…冷媒凝縮部、
11…冷媒圧縮機、13…エアレーシヨンタン
ク。
The drawing is a system explanatory diagram showing an embodiment of the present invention. 1...Water-containing solid matter, 2...Drying room, 3...Air, 4...
Blower, 5...Blower discharge air, 5' high humidity air,
5″...Low temperature, low humidity air, 6...Heat exchanger, 7...Air,
7'... Warm air, 8... Refrigerant evaporation section, 10... Refrigerant condensation section,
11... Refrigerant compressor, 13... Aeration tank.

Claims (1)

【特許請求の範囲】 1 有機性汚水処理において発生する含水物を乾
燥する乾燥室を密閉構造とし、該乾燥室内の空気
をブロワにて吸引し、該ブロワ吐出空気の保有熱
によつて空気を加温し、得られた温風を前記ブロ
ワの吸気によつて前記乾燥室内に吸引して乾燥用
熱源として利用し、その降温したブロワ吐出空気
をヒートポンプの冷媒蒸発部に接触させて冷却、
除湿するとともに該ヒートポンプの冷媒凝縮部か
らの放熱を前記乾燥室における乾燥用熱源として
利用し、さらに前記ヒートポンプの冷媒蒸発部か
ら流出する低温低湿のブロワ吐出空気を有機性汚
水及び又は有機性汚泥の曝気工程にて利用するこ
とを特徴とする含水物の乾燥方法。 2 前記ブロワ本体の発生熱を前記乾燥室内に放
散させるものである特許請求の範囲第1項記載の
含水物の乾燥方法。
[Claims] 1. A drying chamber for drying water-containing substances generated in organic wastewater treatment has a sealed structure, and the air inside the drying chamber is sucked by a blower, and the air is blown by the heat retained in the air discharged from the blower. The heated air is heated, and the obtained warm air is sucked into the drying chamber by the intake air of the blower and used as a heat source for drying, and the cooled blower discharge air is brought into contact with a refrigerant evaporation part of a heat pump to cool it.
In addition to dehumidifying, the heat dissipated from the refrigerant condensing section of the heat pump is used as a heat source for drying in the drying chamber, and the low temperature and low humidity blower discharge air flowing out from the refrigerant evaporating section of the heat pump is used to dehumidify organic sewage and/or organic sludge. A method for drying a hydrated material characterized by use in an aeration process. 2. The method of drying a water-containing material according to claim 1, wherein heat generated by the blower body is dissipated into the drying chamber.
JP58190629A 1983-10-14 1983-10-14 Method of drying hydrous substance Granted JPS6082775A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58190629A JPS6082775A (en) 1983-10-14 1983-10-14 Method of drying hydrous substance

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58190629A JPS6082775A (en) 1983-10-14 1983-10-14 Method of drying hydrous substance

Publications (2)

Publication Number Publication Date
JPS6082775A JPS6082775A (en) 1985-05-10
JPH0245519B2 true JPH0245519B2 (en) 1990-10-09

Family

ID=16261247

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58190629A Granted JPS6082775A (en) 1983-10-14 1983-10-14 Method of drying hydrous substance

Country Status (1)

Country Link
JP (1) JPS6082775A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60107776A (en) * 1983-11-17 1985-06-13 Matsushita Electric Ind Co Ltd tape cassette

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5318854A (en) * 1976-08-06 1978-02-21 Suido Kiko Kk Apparatus for treating to dry sludge
JPS5575989A (en) * 1978-12-04 1980-06-07 Mitsubishi Heavy Ind Ltd Sewerage sludge composting apparatus
JPS5733714A (en) * 1980-08-07 1982-02-23 Jgc Corp Treatment of sludge of waste water treating

Also Published As

Publication number Publication date
JPS6082775A (en) 1985-05-10

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