JP2008188575A - Method for carbonizing and reutilizing volatile residue - Google Patents
Method for carbonizing and reutilizing volatile residue Download PDFInfo
- Publication number
- JP2008188575A JP2008188575A JP2007050521A JP2007050521A JP2008188575A JP 2008188575 A JP2008188575 A JP 2008188575A JP 2007050521 A JP2007050521 A JP 2007050521A JP 2007050521 A JP2007050521 A JP 2007050521A JP 2008188575 A JP2008188575 A JP 2008188575A
- Authority
- JP
- Japan
- Prior art keywords
- carbonization
- residue
- superheated steam
- furnace
- coating
- 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.)
- Pending
Links
Images
Landscapes
- Drying Of Solid Materials (AREA)
- Treatment Of Sludge (AREA)
- Coke Industry (AREA)
Abstract
Description
本発明は、自動車業界や家電業界の製造工場における製品の完成直前に行う塗装工程における吹き付けや電着塗装において、チタンや希少金属を含んだ大量の塗料残渣が汚泥として発生しますが、一般にはこれらの塗装残渣は産業廃棄物汚泥として処理され、最終的には焼却や埋め立て処分されておりますがこれらを無駄に捨てることなく、これらを安全且つ無害に処理することは元より、該塗料糟残渣を有効資源として活用することを目的とする処理方法に関するものである。 In the present invention, a large amount of paint residue containing titanium and rare metals is generated as sludge in spraying and electrodeposition coating in the painting process performed immediately before the completion of the product in the manufacturing factory of the automobile industry and the home appliance industry. These paint residues are treated as industrial waste sludge, and finally are incinerated or landfilled. However, it is important not to dispose of them wastefully but to treat them safely and harmlessly. The present invention relates to a treatment method for the purpose of utilizing the residue as an effective resource.
自動車業界や家電業界の製造工場における製品の最終工程において、車体やフレームなど外装部分の最後の仕上げとして、外装用塗料を吹き付け塗装や電着塗装法などで最終仕上げを行いますが、この塗装の際に大量の塗料残渣汚泥が発生しておりこれら塗料残渣を現状の焼却処理や、産業廃棄物として処理するのでなく、安全且つ無害に処理することは元より、該塗料糟残渣を有効資源として回収し、リサイクルを図る為これら残渣汚泥を焼却の対極の技術とも言うべき炭化処理して回収し再利用する技術を提供するものである。 In the final process of products at manufacturing plants in the automobile industry and the household electrical appliance industry, the final finishing of exterior parts such as car bodies and frames is done by spraying exterior paint or by electrodeposition coating. A large amount of paint residue sludge is generated at the time, and the paint residue is used as an effective resource, not to treat it as a current incineration process or industrial waste, but to treat it safely and harmlessly. In order to recover and recycle, we provide a technology to recover and reuse these residual sludge by carbonization treatment, which can be called the opposite technology of incineration.
自動車や電化製品の表面外装塗装工程において、塗装作業の性質上、塗装の際に1/3〜1/4の余分な塗料即ち塗料残渣又は塗料糟が汚泥として発生しており、現状では当該塗料残渣汚泥は焼却炉で直接焼却処理されるか、産業廃棄物としての処理方法が一般的であり、特許文献などの調査においても先願文献も無く、特に自動車や家電製品などの外装塗装において発生する吹き付け塗料残渣並び塗料汚泥などは、例え汚泥と云えども着火性が良い物質を含有する為、ドラム缶などで一時保管し厳重且つ慎重安全に扱われた後、高い経費と手間を掛けての焼却処理や、産業廃棄物として処理されているものを、資源として回収し再利用する技術を提供せんとするものであり、実質的には処理現場での現状は焼却処理が実情の今日、地球温暖化問題、稀少金属取引に関する国際間の摩擦など、今や塗料残渣の回収技術は貴重な資源確保の点からも重要な問題であります。In the exterior exterior coating process of automobiles and electrical appliances, due to the nature of the painting work, 1/3 to 1/4 of extra paint, i.e., paint residue or paint soot, is generated as sludge during painting. Residual sludge is either directly incinerated in an incinerator or treated as industrial waste, and there is no prior application literature in patent literature or other studies, especially in exterior coatings such as automobiles and home appliances. Spray paint residue and paint sludge, etc., which contain ignitable substances, such as sludge, are temporarily stored in drums, etc., treated with strict and careful safety, and then incinerated with high costs and labor. It is intended to provide technology for recovering and reusing resources that have been treated as industrial wastes as industrial resources. Problem, such as the friction between the international on rare metal trading, now recovery technology of paint residue is an important problem from the viewpoint of valuable resources secured.
本発明はかかる問題点に鑑みてなされたもので、その目的は当該塗料残渣汚泥を廃棄物としてではなく、資源として回収し再利用する手段として、まず水分を取る為一旦乾燥した後、還元雰囲気下での過熱蒸気を利用することによって、爆発や引火の危険性の少ない環境において炭化処理後、回収して再利用することを目的とするものである。The present invention has been made in view of such problems, and its purpose is not to use the paint residue sludge as a waste, but as a means to collect and reuse it as a resource. By using superheated steam below, it is intended to be recovered and reused after carbonization in an environment where there is little risk of explosion or ignition.
上記問題点は下記の手段で解決できる。
1、 塗料残渣並びに塗料汚泥を再利用する為には、前処理としてまず塗料残渣に含有する不純物を除く為磁選機で金属性異物を除き、次に破砕機に掛けことによって当該残渣を出来る限り一定サイズに調整することにより熱効果が均一になるように前処理した後、
2、 次に当該汚泥から水分を抜く為、乾燥炉又は横型キルン炉などでまず一次乾燥しますが、このときの乾燥熱源はバーナーの直接加熱以外にもボイラーの廃熱や過熱炉の廃熱を利用しても良い。この時当該残渣に含有するプラスチック系の包装資材や有機性廃棄物は水分と一緒に炉内温度約120℃以上300℃前後でまず気化させる。
3、 次の工程の炭化炉ではまず炉内に280℃以上の過熱蒸気を一定時間、炉内に吹き込むことにより炉内の酸素が極少となり還元雰囲気に近い状態になり、且つ炉内雰囲気温度が少なくとも200℃以上になった後、乾燥処理後の塗料残渣汚泥を当該炉内に投入する。
4、 この時の熱処理工程に過熱蒸気を使うことにより、塗料残渣に付着若しくは含有する廃プラスチック系などが気化することにより発生する炭化炉内の可燃性の熱分解ガスも、炉内が過熱蒸気という不活性ガス体で充満しているため、例え高温下であっても爆発や引火の危険も無く安全に処理が可能となる。
5、 その為にはまずボイラーで100℃の飽和蒸気を生成した後、次に飽和蒸気を過熱炉(過熱蒸気発生器)で再加熱することによって300℃〜800℃の過熱蒸気を生成する。生成した過熱蒸気を前述の還元雰囲気下且つ高温状態に維持された乾燥炉や横型キルン炉に吹き込むと同時に塗料汚泥も投入し一定時間炉内の還元雰囲気下での過熱蒸気に暴露することにより塗料残渣の炭化が進む。
6、 次に炭化炉内温度を300℃ら600℃前後に上げると紙などの挟雑物、あるいはその他の有機性混入物は炉内に酸素がない為、気化又は熱分解し目的とする塗料残渣のみが酸化する事無く回収できる。
7、 尚乾燥工程における乾燥熱源として経費節減のため、当該汚泥の含水率が20%程度まではボイラーなどの廃熱を有効利用しても良い。The above problems can be solved by the following means.
1. In order to reuse paint residue and paint sludge, as a pre-treatment, first remove the metallic foreign matter with a magnetic separator to remove impurities contained in the paint residue, and then apply the residue to the crusher as much as possible. After pre-processing so that the thermal effect is uniform by adjusting to a certain size,
2. Next, in order to remove moisture from the sludge, primary drying is first performed in a drying furnace or horizontal kiln furnace. The heat source for drying at this time is not only the direct heating of the burner but also the waste heat of the boiler and the waste heat of the superheated furnace. May be used. At this time, the plastic packaging material and organic waste contained in the residue are first vaporized together with moisture at a furnace temperature of about 120 ° C. or more and about 300 ° C.
3. In the carbonization furnace in the next step, first, superheated steam of 280 ° C or higher is blown into the furnace for a certain period of time, so that the oxygen in the furnace becomes minimal and the atmosphere is close to the reducing atmosphere. After at least 200 ° C. or higher, the paint residue sludge after the drying treatment is put into the furnace.
4. By using superheated steam for the heat treatment process at this time, the combustible pyrolysis gas in the carbonization furnace generated by vaporizing the waste plastic system attached to or contained in the paint residue is also superheated steam. Because it is filled with an inert gas body, it can be processed safely without danger of explosion or ignition even at high temperatures.
5. To that end, first, a saturated steam at 100 ° C. is generated by a boiler, and then the superheated steam at 300 ° C. to 800 ° C. is generated by reheating the saturated steam in a superheated furnace (superheated steam generator). The generated superheated steam is blown into a drying furnace or horizontal kiln furnace maintained at a high temperature under the above-mentioned reducing atmosphere, and at the same time, paint sludge is introduced and exposed to the superheated steam in the reducing atmosphere in the furnace for a certain period of time. Carbonization of the residue proceeds.
6. Next, if the temperature in the carbonization furnace is raised from 300 ° C to around 600 ° C, paper and other foreign substances or other organic contaminants will not have oxygen in the furnace, so they will be vaporized or thermally decomposed to the desired paint. Only the residue can be recovered without being oxidized.
7. In order to reduce costs as a drying heat source in the drying process, waste heat from a boiler or the like may be effectively used until the water content of the sludge is about 20%.
1、 廃棄物として処理されていた塗料残渣の大部分を捨てることなく還元雰囲気下で過熱蒸気を使って炭化することによって、ほとんど劣化しない再生品として再利用、若しくは増量剤としての利用が可能となり、炭化に要する費用も廃棄処理費用以下で可能であり、経費節減はもとより資源の有効利用が可能となり、且つ焼却処理という地球温暖化問題など環境上の問題にも一助となった。1. Carbonization using superheated steam in a reducing atmosphere without throwing away most of the paint residue that has been treated as waste makes it possible to reuse it as a recycled product that hardly deteriorates or as an extender. In addition, the cost required for carbonization can be less than the disposal cost, and not only the cost can be saved, but also the resources can be used effectively, and it has helped to environmental problems such as the global warming problem of incineration.
本発明の炭化炉とその実施例を図面で説明する。
図1は全体のフロー図であります
図2は、本発明の縦型バッチの実施例説明図です。The carbonization furnace of the present invention and its embodiments will be described with reference to the drawings.
FIG. 1 is an overall flow diagram. FIG. 2 is an explanatory diagram of an embodiment of a vertical batch according to the present invention.
図2は縦型バッチの炭化炉であり炉体キャビティーの周囲並びに上部と底面の内部壁全面を断熱材で囲まれた構造からなり、上部正面に設けた乾燥室投入口7から、炭化対象物である塗料残渣汚泥約30kgを6個の平型バット容器に分けそのまま炉内に直接容器ごと投入する。乾燥室では燃焼室からの排ガスが循環する為、処理対象物が乾燥し、次の下方炭化室に送り込まれる。尚本実施例は回転式キルン炉に変わり縦型ゆえ炉床が回転します。FIG. 2 shows a vertical batch carbonization furnace, which has a structure in which the periphery of the furnace body cavity and the entire inner walls of the upper and bottom surfaces are surrounded by a heat insulating material. About 30 kg of paint residue sludge, which is a product, is divided into six flat bat containers and directly put into the furnace as it is. Since the exhaust gas from the combustion chamber circulates in the drying chamber, the object to be treated is dried and fed into the next lower carbonization chamber. In this embodiment, the hearth is rotated because it is a vertical type instead of a rotary kiln furnace.
乾燥室に投入した含水率約80%の塗料残渣汚泥を投入後、乾燥室投入口7を閉めてバーナーのスイッチ1を入れ、まず炉内の加温と同時にボイラー(飽和蒸気発生装置)6を温め飽和蒸気を生成する。飽和蒸気は、バーナーの燃焼室天井部に設置された蛇管型の過熱蒸気発生装置5を経由し、炭化室下部の過熱蒸気噴射口から噴射されろことにより炭化室の温度は、概ね350℃〜600℃に加熱昇温される。即ち過熱水蒸気は、ボイラー6(飽和水蒸気生成装置)で生成された飽和水蒸気が5の過熱水蒸気生成装置を経ることにより過熱水蒸気に変わり炭化室12内に下部から噴出する。After the paint residue sludge with a water content of about 80% is charged in the drying chamber, the drying chamber inlet 7 is closed and the
キャビティーの中は過熱蒸気の吹込みにより炉内酸素が追い出され、無酸素状態の還元雰囲気、且つ400℃〜500℃の温度帯の過熱水蒸気雰囲気で30kgの塗料残渣汚泥を約2時間炭化した結果、炉内に投入した塗料残渣汚泥は途中約1時間での状態ではぽろぽろとなり、2時間経過の結果はさらさらの粉末状の良質な炭化物となった。特に臭気に於いては臭気のきついブチルアルコール、キシレン、トルエンなども熱分解され無臭であった。又炭化した結果の生成炭化物について、数値的には30kgの塗料残渣汚泥が1.5kgとなり重量的には0.5%に減量したが容積は約1/10であった。炭化物はそのままペール缶に保管した。Oxygen in the furnace was expelled by blowing superheated steam into the cavity, and 30 kg of paint residue sludge was carbonized for about 2 hours in an oxygen-free reducing atmosphere and a superheated steam atmosphere in the temperature range of 400 ° C to 500 ° C. As a result, the paint residue sludge charged into the furnace became muddy in the state of about 1 hour on the way, and the result after 2 hours became a fine powdery carbide in smooth powder. In particular, in terms of odor, butyl alcohol, xylene, toluene and the like having a strong odor were thermally decomposed and odorless. In addition, regarding the resulting carbide as a result of carbonization, 30 kg of paint residue sludge was numerically reduced to 1.5 kg and reduced in weight to 0.5%, but the volume was about 1/10. The carbide was stored in a pail as it was.
上記の炭化実証においての
灯油の使用量:7リットル/時間、2時間で14リットルを使用した。
各部の温度 :バーナー加熱部800℃でコントロール
上記炭化による8]排気ガスについて特に異常な臭気や煙などの異常は無煙無臭の排気ガスで、安全にしかも廉価で炭化処理が出来ることの可能性が証明された。Amount of kerosene used in the above carbonization demonstration: 7 liters / hour, 14 liters were used for 2 hours.
Temperature of each part: Control by burner heating section 800 ° C 8) Due to the above carbonization Exhaust gas especially abnormal odors and smoke abnormalities are smokeless and odorless exhaust gas, and there is a possibility that it can be carbonized safely and inexpensively Proven.
以上、詳記した様に本発明はわざわざ高い経費をかけて焼却処理若しくは廃棄処分として処理されている塗料糟汚泥を、廃棄することなく安全に且つ廉価で、再生品やバージンの増量材としても利用可能な炭化物として回収再生する、画期的な新規資源の確保はもとより革新的な技術であり新産業勃興に多大の貢献をなすものである。As described above in detail, the present invention can be used as a recycle product or a virgin extender, safely and inexpensively without disposing of paint sludge that has been treated as an incineration process or a disposal process at a high cost. It is an innovative technology as well as ensuring innovative new resources that can be recovered and recycled as usable carbides, and it contributes greatly to the rise of new industries.
Claims (3)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2007050521A JP2008188575A (en) | 2007-02-01 | 2007-02-01 | Method for carbonizing and reutilizing volatile residue |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2007050521A JP2008188575A (en) | 2007-02-01 | 2007-02-01 | Method for carbonizing and reutilizing volatile residue |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2008188575A true JP2008188575A (en) | 2008-08-21 |
Family
ID=39749185
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2007050521A Pending JP2008188575A (en) | 2007-02-01 | 2007-02-01 | Method for carbonizing and reutilizing volatile residue |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2008188575A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101475862A (en) * | 2009-01-21 | 2009-07-08 | 李兴 | Method for making carbon rod by charing sludge |
-
2007
- 2007-02-01 JP JP2007050521A patent/JP2008188575A/en active Pending
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101475862A (en) * | 2009-01-21 | 2009-07-08 | 李兴 | Method for making carbon rod by charing sludge |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2010106133A (en) | Process and apparatus for making waste into fuel | |
CN108911456B (en) | Novel oily sludge treatment method and system | |
EP3012037A1 (en) | Production line and method for recycling of charcoal and gas from garbage | |
CN104006390B (en) | A kind of method of cement plant cooperative disposal garbage power | |
JP2009013388A (en) | Carbonizing recycling method for volatile residue | |
JP2008188575A (en) | Method for carbonizing and reutilizing volatile residue | |
JP2009072749A (en) | Method for drying, carbonizing and reutilizing painting residue sludge | |
JP4440696B2 (en) | Carbonization method of sewage sludge | |
JP4231739B2 (en) | Sludge recycling method | |
WO2019009073A1 (en) | Resource recovery/recycling facility using superheated steam | |
JP2009161845A (en) | Method for pretreatment of scrap | |
JPH11159718A (en) | Device and method for combustion | |
KR200393812Y1 (en) | Recycling system of waste paint | |
KR101416679B1 (en) | Carbonization device using high frequency for food waste and industrial waste | |
JP2012125666A (en) | Device for treating metal scrap | |
JPH10110929A (en) | Method for processing waste fluorocarbon | |
CN112393246A (en) | Harmless treatment method for hazardous waste | |
TWM575723U (en) | Solid, gaseous, liquid organic compound processing system | |
JP3982040B2 (en) | Method and apparatus for treating halogen-containing materials | |
JP2002310418A (en) | Method for treating waste | |
JP2002088372A (en) | Method for utilizing organic waste | |
WO2009081434A2 (en) | Process and apparatus for the disposal of refuse containing metals, inert and organic fractions | |
JP2006326383A (en) | Method of recycling disused car | |
JPH1176978A (en) | Treatment of waste rubber-metal composite material | |
WO2021038308A1 (en) | A system and method for treatment of waste materials |