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JP6718354B2 - Incineration treatment method of waste - Google Patents
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JP6718354B2 - Incineration treatment method of waste - Google Patents

Incineration treatment method of waste Download PDF

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JP6718354B2
JP6718354B2 JP2016193798A JP2016193798A JP6718354B2 JP 6718354 B2 JP6718354 B2 JP 6718354B2 JP 2016193798 A JP2016193798 A JP 2016193798A JP 2016193798 A JP2016193798 A JP 2016193798A JP 6718354 B2 JP6718354 B2 JP 6718354B2
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drum
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裕樹 長村
裕樹 長村
和寛 湯谷
和寛 湯谷
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Dowa Eco Systems Co Ltd
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Description

本発明は、可燃物を含む廃棄物の焼却処理方法に関する。 The present invention relates to a method for incinerating waste containing combustible substances.

現在使用が禁止されている有害なPCBを含有する廃棄物は、専用の焼却炉において焼却処理されることで無害化される。PCB含有廃棄物の焼却処理方法として、特許文献1には、PCB含有廃棄物を上方が開放されたドラム缶等の容器に収容し、その状態でドラム缶を炉内に搬入して加熱処理を行う方法が開示されている。 Wastes containing harmful PCBs which are currently prohibited from use are detoxified by being incinerated in a dedicated incinerator. As a method for incinerating PCB-containing waste, Patent Document 1 discloses a method in which PCB-containing waste is stored in a container such as a drum can whose upper side is open, and in that state, the drum can is carried into a furnace for heat treatment. Is disclosed.

ところで、PCBを含有する廃棄物には、絶縁紙とアルミ箔で構成されるコンデンサ素子などの可燃物を多く含有するものがある。例えば素子中の絶縁紙には、PCB汚染油が含浸されており、焼却処理時の発熱量が大きくなる。このような可燃物を含む廃棄物を一度に大量に焼却炉に搬入すると、燃焼反応による発熱量が大きくなりすぎてしまう。その結果、焼却炉の許容温度の上限を超過した高温状態となり、焼却炉の炉材が劣化、損傷するおそれがある。また、急激な燃焼反応による一時的な酸素の欠乏によって、炉内のCO濃度の上昇を招き、CO濃度を低減させるための排ガス処理の負荷が増大することも懸念される。 By the way, as a waste material containing PCB, there is a waste material containing a large amount of combustible material such as a capacitor element composed of insulating paper and aluminum foil. For example, the insulating paper in the element is impregnated with PCB contaminated oil, and the amount of heat generated during incineration becomes large. If a large amount of waste containing such combustibles is carried into the incinerator at once, the amount of heat generated by the combustion reaction becomes too large. As a result, the temperature of the incinerator exceeds the upper limit of the allowable temperature, and the furnace material of the incinerator may deteriorate or be damaged. Further, there is a concern that a temporary lack of oxygen due to a rapid combustion reaction may lead to an increase in the CO concentration in the furnace and an increase in the exhaust gas treatment load for reducing the CO concentration.

それらの問題を未然に防ぐ手法として、特許文献2には可燃物の導入路に散水装置を備えた焼却処理装置が開示されている。特許文献2では可燃物への散水量を調節することで過剰燃焼の抑制を図っている。 As a method of preventing those problems, Patent Document 2 discloses an incineration treatment device provided with a sprinkler device in a passage for introducing combustible materials. In Patent Document 2, excessive combustion is suppressed by adjusting the amount of water sprayed on the combustible material.

特開2011−56504号公報JP, 2011-56504, A 特開2016−90148号公報JP, 2016-90148, A

しかしながら、特許文献2の焼却処理装置は、散水により廃棄物の燃焼開始時期を遅らせることはできるが、同一のタイミングで焼却処理装置に投入された廃棄物の燃焼は、廃棄物の投入後、同時期に開始されることになる。したがって、特許文献2の焼却処理装置を以てしても、同一のタイミングで投入された廃棄物は、依然として一度に大量に燃焼されることになる。このため、前述のような焼却炉の炉材の劣化や損傷、CO濃度の上昇に起因する排ガス処理の負荷の増大といった懸念事項は解消されない。 However, the incinerator of Patent Document 2 can delay the combustion start timing of the waste by sprinkling water, but the combustion of the waste put into the incinerator at the same timing is the same after the waste is put in. It will be started in time. Therefore, even with the incineration treatment device of Patent Document 2, a large amount of waste that is input at the same timing is still burned at once. Therefore, such concerns as deterioration and damage of the furnace material of the incinerator and an increase in the load of exhaust gas treatment due to an increase in CO concentration cannot be resolved.

本発明は、上記事情に鑑みてなされたものであり、可燃物を含む廃棄物の焼却処理において、焼却炉に搬入された廃棄物が一度に大量に燃焼することを抑制することを目的とする。 The present invention has been made in view of the above circumstances, and it is an object of the present invention to suppress a large amount of the waste carried into an incinerator from being burned at once in the incineration of waste containing combustible materials. ..

上記課題を解決する本発明は、可燃物を含む廃棄物の焼却処理方法であって、貯液性を有し、かつ開口部を有した、複数の収容領域それぞれに該廃棄物が収容され、かつ各収容領域内の沸騰性液体の量がそれぞれ異なる状態となるように前記沸騰性液体が前記収容領域に入れられることで構成される焼却対象単位を焼却炉に搬入し、前記廃棄物の焼却処理を行うことを特徴としている。 The present invention for solving the above-mentioned problems is a method for incineration of waste containing combustible material, which has a liquid storage property and has an opening, and the waste is stored in each of a plurality of storage areas, And, the incineration target unit configured by putting the boiling liquid in the storage area so that the amounts of the boiling liquid in the storage areas are different from each other is carried into an incinerator, and the waste is incinerated. It is characterized by performing processing.

本発明によれば、可燃物を含む廃棄物の焼却処理において、焼却炉に搬入された廃棄物が一度に大量に燃焼することを抑制することができる。 ADVANTAGE OF THE INVENTION According to this invention, in the incineration process of the waste containing a combustible material, it can suppress that the waste carried into the incinerator burns in large quantities at once.

本発明の実施形態に係る焼却炉の概略構成を示す図である。It is a figure which shows schematic structure of the incinerator which concerns on embodiment of this invention. 本発明の実施形態に係る廃棄物の収容状態を示す図である。It is a figure which shows the accommodation state of the waste material which concerns on embodiment of this invention.

以下、本発明の一実施形態について、図面を参照しながら説明する。なお、本明細書および図面において、実質的に同一の機能構成を有する要素においては、同一の符号を付することにより重複説明を省略する。 An embodiment of the present invention will be described below with reference to the drawings. In the present specification and the drawings, elements having substantially the same functional configuration are designated by the same reference numerals, and duplicate description will be omitted.

本実施形態ではPCBを含有する廃棄物の焼却処理を例に挙げて説明する。まず、廃棄物Wを焼却する焼却炉10は、図1に示すように加熱処理前の廃棄物Wが待機する搬入待機室11と、廃棄物Wの加熱処理を行う処理室12と、加熱処理後の廃棄物Wが待機する搬出待機室13を備えている。搬入待機室11と処理室12の間、および、処理室12と搬出待機室13との間には開閉自在な扉14が設けられている。 In the present embodiment, the incineration process of waste containing PCB will be described as an example. First, as shown in FIG. 1, the incinerator 10 for incinerating the waste W has a carry-in standby chamber 11 in which the waste W before the heat treatment stands by, a treatment chamber 12 for performing the heat treatment of the waste W, and a heat treatment. It is provided with a carry-out waiting chamber 13 in which the later waste W stands by. Doors 14 that can be opened and closed are provided between the carry-in waiting chamber 11 and the processing chamber 12 and between the processing chamber 12 and the carrying-out waiting chamber 13.

処理室12は、廃棄物Wを加熱する昇温部12aと、加熱された廃棄物Wの温度を保持する温度保持部12bと、廃棄物Wを冷却する冷却部12cとを有している。また、処理室12の昇温部12aには、処理室内で発生する排ガスを排気する排気管15が接続されている。廃棄物Wは、台車2に載せられた上部が開放された状態のドラム缶3に収容されている。なお、図1では焼却炉10の構造を説明するために、1つのドラム缶3が台車2に載せられた状態を簡易的に示しているが、より詳細に説明すると、図2のように台車2に3つのドラム缶3が載せられている。 The processing chamber 12 includes a temperature raising unit 12a that heats the waste W, a temperature holding unit 12b that holds the temperature of the heated waste W, and a cooling unit 12c that cools the waste W. An exhaust pipe 15 for exhausting exhaust gas generated in the processing chamber is connected to the temperature raising section 12a of the processing chamber 12. The waste W is stored in the drum can 3 placed on the trolley 2 and having an open upper portion. Note that, in FIG. 1, a state in which one drum 3 is placed on the trolley 2 is simply shown in order to explain the structure of the incinerator 10, but in more detail, as shown in FIG. There are three drums 3 mounted on.

次に、本実施形態に係る廃棄物の焼却処理方法について説明する。 Next, a waste incineration method according to the present embodiment will be described.

まず、図2に示すように3つのドラム缶それぞれに廃棄物Wを収容し、各ドラム缶3を台車2に載せる。本実施形態においては、3つのドラム缶3に収容される廃棄物Wの合計量が従来の台車1台分に載せる廃棄物の量と等しくなっている。 First, as shown in FIG. 2, the waste W is stored in each of the three drums, and each drum 3 is placed on the trolley 2. In this embodiment, the total amount of waste W stored in the three drums 3 is equal to the amount of waste placed on one conventional truck.

続いて、3つのドラム缶3のうち、2つのドラム缶3に水を入れる。このとき、2つのドラム缶3に入れる水の量を互いに異なる量とする。一方で、残りの1つのドラム缶3には水を入れない。このようにして、廃棄物Wが収容される各ドラム缶内の水の量を互いに異なる状態とする。以下の説明では、廃棄物Wが収容され、かつ水の量が互いに異なる状態となった3つのドラム缶3を総称して“焼却対象単位U”という。本実施形態における廃棄物の処理方法では、複数の焼却対象単位Uが設けられ、各焼却対象単位Uが順次焼却炉10に搬入されていく。また、以下の説明では、水が入っていないドラム缶3を第1のドラム缶3a、水が入っている2つのドラム缶3のうち、水の量が少ない方のドラム缶3を第2のドラム缶3b、水の量が多い方のドラム缶3を第3のドラム缶3cと称する。また、第1のドラム缶3aに収容されている廃棄物を第1の廃棄物W、第2のドラム缶3bに収容されている廃棄物を第1の廃棄物W、第3のドラム缶3cに収容されている廃棄物を第3の廃棄物Wと称する。 Then, water is put into two drums 3 among the three drums 3. At this time, the amounts of water put into the two drums 3 are different from each other. On the other hand, the remaining one drum 3 is not filled with water. In this way, the amounts of water in the drums containing the waste W are made different from each other. In the following description, the three drums 3 in which the waste W is stored and the amounts of water are different from each other are collectively referred to as “incineration target unit U”. In the method of treating waste according to the present embodiment, a plurality of incineration target units U are provided, and each incineration target unit U is sequentially carried into the incinerator 10. Further, in the following description, the drum can 3 containing no water is the first drum can 3a, and the drum can 3 having the smaller amount of water out of the two drums 3 containing water is the second drum can 3b. The drum can 3 having the larger amount is referred to as a third drum can 3c. Moreover, waste contained in the first drum 3a first waste W 1, the waste contained in the second drum 3b first waste W 2, the third drum 3c The stored waste is referred to as a third waste W 3 .

各ドラム缶3の水の量がそれぞれ異なる状態のまま、焼却炉内に台車2が搬入され、焼却対象単位Uは搬入待機室11を介して処理室12に到達する。ここで各ドラム缶内の廃棄物Wが加熱されることになる。このとき、第1の廃棄物Wは、第1のドラム缶3a内において処理室内の雰囲気に接した状態にあり、第2の廃棄物Wおよび第3の廃棄物Wに先立って燃焼が開始される。一方、第2の廃棄物Wおよび第3の廃棄物Wは、それぞれ第2のドラム缶3b内および第3のドラム缶3cの内部に水蒸気が満たされた状態にあり、第2の廃棄物Wおよび第3の廃棄物Wの燃焼は開始されない。ただし、第2のドラム缶3bおよび第3のドラム缶3cの水は加熱されることで蒸発速度が速まり、水量が減っていく。この間に第1の廃棄物Wに含まれる可燃物の燃焼により第1のドラム缶3aにおける発熱量が大きくなるが、ドラム缶1つ分の廃棄物の過剰燃焼であるため、台車1台あたりの過剰燃焼による発熱量は従来よりも小さくなっている。 While the amount of water in each drum 3 is different, the truck 2 is loaded into the incinerator, and the incineration target unit U reaches the processing chamber 12 via the loading standby chamber 11. Here, the waste W in each drum can is heated. At this time, the first waste W 1 is in contact with the atmosphere in the processing chamber inside the first drum 3 a, and is burned prior to the second waste W 2 and the third waste W 3. Be started. On the other hand, the second waste W 2 and the third waste W 3 are in a state in which the inside of the second drum 3 b and the inside of the third drum 3 c are filled with water vapor, respectively, and the second waste W 2 The combustion of the second and third waste W 3 is not started. However, by heating the water in the second drum can 3b and the third drum can 3c, the evaporation rate is increased and the amount of water is reduced. During this period, the amount of heat generated in the first drum 3a increases due to the combustion of combustible substances contained in the first waste W 1 , but since the waste of one drum can is excessively burned, the excess amount per trolley. The amount of heat generated by combustion is smaller than before.

第2のドラム缶3bに貯留する水の蒸発が進行し、第2のドラム缶3bに貯留されていた水が無くなると、第2の廃棄物Wの温度がさらに上昇して、燃焼が開始される。この頃には、第1の廃棄物Wの過剰燃焼による発熱量が最大となる燃焼のピークは過ぎている。このため、第2のドラム缶3bの水が更に蒸発し、第2の廃棄物Wが燃焼のピークを迎える頃には、第1の廃棄物Wの発熱量は小さくなっているか、燃焼自体が既に終了している。一方、第2のドラム缶3bよりも多くの水が貯留している第3のドラム缶3cでは依然として水が残った状態にあり、第3の廃棄物Wの燃焼は開始されない。 Evaporation of water proceeds for storing the second drum 3b, the water which has been stored in the second drum 3b is eliminated, and the second waste W temperature of 2 increases further, the combustion is started .. By this time, the peak of combustion at which the amount of heat generated by the excessive combustion of the first waste W 1 is maximized has passed. Therefore, water is further evaporated in the second drum 3b, by the time the second waste W 2 is to peak of combustion, the calorific value of the first waste W 1 is smaller or the combustion itself Has already ended. On the other hand, in the third drum can 3c in which more water is stored than in the second drum can 3b, the water still remains, and the combustion of the third waste W3 is not started.

そして、第3のドラム缶3cの水の蒸発が進行し、第3のドラム缶3cに貯留されていた水が無くなると、第3の廃棄物Wの温度がさらに上昇して、燃焼が開始される。この頃には、第2の廃棄物Wの燃焼のピークは過ぎている。このため、第3のドラム缶3cの水が更に蒸発し、第3の廃棄物Wが燃焼のピークを迎える頃には、第2の廃棄物Wの発熱量は小さくなっているか、燃焼自体が既に終了している。 Then, the water of the third drum 3c evaporation proceeds, the water which has been stored in the third drum 3c is eliminated, a third waste W 3 temperature further rises, the combustion is started .. By this time, the peak of combustion of the second waste W 2 has passed. Therefore, water is further evaporated in the third drum 3c, by the time the third waste W 3 is peaking of combustion or calorific value of the second waste W 2 is smaller, the combustion itself Has already ended.

その後、処理室12を通過する間に第3の廃棄物Wの燃焼も終了し、搬出待機室13を介して焼却対象単位Uが炉外に搬出される。 Then, the combustion of the third waste W 3 is completed while passing through the processing chamber 12, and the unit U to be incinerated is carried out of the furnace via the carry-out waiting chamber 13.

このように、本実施形態に係る廃棄物の焼却処理方法では、廃棄物Wを3つのドラム缶3に分けて収容し、各ドラム缶内の水の量を異なる量とした状態で廃棄物Wを焼却炉に搬入する。この状態で廃棄物の焼却処理を行うことにより、各ドラム缶3に収容された廃棄物Wの燃焼ピークの発生タイミングをずらすことが可能となる。即ち、同一のタイミングで搬入された廃棄物Wが一度に大量に燃焼することを回避することができ、廃棄物の同時燃焼による過大な発熱に起因する炉材の劣化や損傷を抑えることができる。また、急激な燃焼反応を抑えることができるため、CO濃度の上昇を抑えることができ、排ガス処理の負荷を軽減することが可能となる。 As described above, in the waste incineration treatment method according to the present embodiment, the waste W is divided into three drums 3 and accommodated, and the waste W is incinerated while the amount of water in each drum is different. Bring it into the furnace. By incinerating the waste in this state, it is possible to shift the generation timing of the combustion peak of the waste W stored in each drum 3. That is, it is possible to avoid a large amount of the waste W that is carried in at the same timing from burning at once, and it is possible to suppress deterioration or damage of the furnace material due to excessive heat generation due to simultaneous combustion of the waste. .. Further, since the rapid combustion reaction can be suppressed, the increase in CO concentration can be suppressed, and the load of exhaust gas treatment can be reduced.

また、本実施形態に係る廃棄物の焼却処理方法では、各ドラム缶3に収容された廃棄物Wの燃焼ピークの発生タイミングを自在に制御することができるため、例えば焼却炉の内面炉材のうち燃焼ガスによる劣化が進みやすい箇所において燃焼ピークが発生しないようにコントロールをするなどして焼却炉全体としての延命化を図る等の応用も可能である。 Further, in the waste incineration processing method according to the present embodiment, since the generation timing of the combustion peak of the waste W stored in each drum 3 can be freely controlled, for example, among the inner furnace materials of the incinerator, Applications such as extending the life of the incinerator as a whole by controlling so that combustion peaks do not occur at locations where deterioration due to combustion gas is likely to proceed are possible.

なお、本実施形態ではPCBを含有する廃棄物を焼却処理対象物としたが、焼却処理対象物は、可燃物を含む廃棄物であれば、PCBを含有しないものであっても良い。 In the present embodiment, the waste containing PCB is the incineration target, but the incineration target may not contain PCB as long as it is a waste containing a combustible material.

また、本実施形態では3本のドラム缶のうち、1本のドラム缶には水を入れていないが、ドラム缶が複数用いられる場合には全てのドラム缶に水を入れても良い。この場合であっても、各ドラム缶の水の量が互いに異なっていれば、各廃棄物の燃焼開始時期をずらすことは可能である。 Further, in the present embodiment, one of the three drums does not contain water, but when a plurality of drums are used, water may be contained in all the drums. Even in this case, if the amount of water in each drum is different from each other, it is possible to shift the combustion start timing of each waste.

また、本実施形態ではドラム缶3に水を入れることとしたが、ドラム缶3に入れるものは水に限定されない。沸点が焼却炉の炉外温度よりも高く、炉内温度よりも低い、不燃性の液体または液状含水物であれば良い。本発明においては、このような液体または液状含水物を“沸騰性液体”と称する。なお、炉や排ガス、焼却処理に与える影響がなく、量の調節が容易であるという観点から、沸騰性液体は水であることが好ましい。また、各ドラム缶3に入れる沸騰性液体の量は、沸騰性液体として用いる液体の種類や炉内における沸騰性液体の蒸発の早さに応じて適宜変更されるものであるが、1つのドラム缶内の廃棄物が十分に燃焼してから、他のドラム缶内の廃棄物の燃焼が開始されるような量に調節することが好ましい。 Further, although water is put in the drum can 3 in the present embodiment, what is put in the drum can 3 is not limited to water. Any non-combustible liquid or liquid hydrate having a boiling point higher than the temperature outside the furnace of the incinerator and lower than the temperature inside the furnace may be used. In the present invention, such liquid or liquid hydrate is referred to as "boiling liquid". The boiling liquid is preferably water from the viewpoint that it has no effect on the furnace, the exhaust gas, and the incineration process and the amount can be easily adjusted. Further, the amount of the boilable liquid to be put into each drum 3 is appropriately changed according to the type of the liquid used as the boilable liquid and the speed of evaporation of the boilable liquid in the furnace. It is preferable to adjust the amount so that the waste in the other drums starts to burn before the waste in the other drums starts to burn.

また、本実施形態では上部が開放された状態のドラム缶3に廃棄物Wを収容することとしたが、収容する容器について必ずしも上部の全面が開放されている必要はなく、炉室内で沸騰性液体が蒸発した際に、蒸発したガスが容器から排出されるための開口部が設けられていればよい。さらにまた、廃棄物Wを収容する容器はドラム缶3に限定されず、他の容器であっても良い。なお、水を入れやすく、搬送しやすいという観点からは上部が開放された容器であることが好ましい。 Further, in the present embodiment, the waste W is stored in the drum 3 whose upper part is opened, but the entire upper part of the container to be stored does not necessarily have to be open, and the boiling liquid in the furnace chamber is not necessarily opened. It suffices to provide an opening for discharging the evaporated gas from the container when the gas is evaporated. Furthermore, the container for storing the waste W is not limited to the drum 3 and may be another container. It is preferable that the container has an open upper portion from the viewpoint of easy water filling and easy transportation.

また、本実施形態では、廃棄物を3本のドラム缶3に分けて収容することとしたが、ドラム缶3の本数はこれに限定されない。また、1本のドラム缶3の内部を仕切り、そのドラム缶3の中に廃棄物を収容する複数の収容領域を設けるようにしても良い。この場合であっても、各収容領域に沸騰性液体が貯えられ、沸騰性液体は炉内での時間の経過により蒸発して、量が減っていき、液体が無くなったタイミングで燃焼が開始する。即ち、各収容領域は沸騰性液体を貯留することが可能な貯液性を有する構造となっていれば良い。ただし、燃焼時期をずらすという目的を阻害しない範囲で沸騰性液体の流出や流入は許容される。なお、1本のドラム缶の内部を仕切って複数の収容領域を設ける場合には、各収容領域に廃棄物が収容され、かつ各収容領域の沸騰性液体の量が互いに異なる状態となった1本のドラム缶が焼却対象単位となる。即ち、“焼却対象単位”とは、貯液性を有し、かつ開口部を有した、複数の収容領域それぞれに該廃棄物が収容されており、かつ各収容領域内の沸騰性液体の量がそれぞれ異なる状態となるように前記沸騰性液体が前記収容領域に入れられている、収容領域のまとまりのことである。 Further, in the present embodiment, the waste is divided into three drums 3 to be stored, but the number of the drums 3 is not limited to this. Alternatively, the inside of one drum can 3 may be partitioned and a plurality of storage areas for storing waste may be provided in the drum can 3. Even in this case, the boiling liquid is stored in each accommodation area, the boiling liquid evaporates with the passage of time in the furnace, the amount decreases, and the combustion starts at the timing when the liquid runs out. .. That is, each accommodation area may have a structure having a liquid storage property capable of storing the boiling liquid. However, outflow or inflow of the boiling liquid is allowed within a range that does not impair the purpose of shifting the combustion timing. When partitioning the inside of one drum to provide a plurality of storage areas, waste is stored in each storage area, and the amount of the boiling liquid in each storage area is different from each other. The drums will be the unit to be incinerated. That is, the "incineration target unit" means that the waste is stored in each of a plurality of storage areas having a liquid storage property and having an opening, and the amount of the boiling liquid in each storage area. Is a group of accommodation areas in which the boilable liquid is contained in the accommodation area so that the respective states are different.

以上の点に鑑みると、廃棄物が一度に大量に燃焼することを抑制するためには、貯液性を有し、かつ開口部を有した、複数の収容領域それぞれに該廃棄物を収容し、かつ各収容領域内の沸騰性液体の量がそれぞれ異なる状態となるように収容領域に沸騰性液体を入れることで構成される焼却対象単位を焼却炉に搬入して焼却処理を実施すれば良い。なお、焼却炉の構造は本実施形態で説明したものに限定されない。例えば各部屋が仕切られておらず、焼却対象単位が途中で停止せずに移動し続ける構成の炉であっても良い。この場合でも、焼却対象単位内では廃棄物が異なるタイミングで燃焼するため、上記実施形態と同様に廃棄物が一度に大量に燃焼することを回避することができる。 In view of the above points, in order to prevent a large amount of waste from being burned at once, the waste is stored in each of a plurality of storage areas having a liquid storage property and having an opening. And, the incineration target unit configured by putting the boiling liquid in the storage area so that the amount of the boiling liquid in each storage area is different may be carried into the incinerator to perform the incineration process. .. The structure of the incinerator is not limited to that described in this embodiment. For example, the furnace may be configured such that each room is not partitioned and the unit to be incinerated continues to move without stopping halfway. Even in this case, since the wastes are burned at different timings within the unit to be incinerated, it is possible to avoid burning a large amount of the wastes at the same time as in the above embodiment.

また、本実施形態では、廃棄物Wを台車2で搬送することとしたが、搬送機構はこれに限定されない。廃棄物Wや水がこぼれにくい状態で焼却処理を行うことができるという観点からは搬送機構として台車を用いることが好ましい。 Further, in the present embodiment, the waste W is transported by the carriage 2, but the transport mechanism is not limited to this. From the viewpoint that the incineration process can be performed in a state in which the waste W or water is unlikely to spill, it is preferable to use a trolley as the transport mechanism.

以上、本発明の実施形態について説明したが、本発明はかかる例に限定されない。当業者であれば、特許請求の範囲に記載された技術的思想の範疇内において、各種の変更例または修正例に想到しうることは明らかであり、それらについても当然に本発明の技術的範囲に属するものと了解される。 Although the embodiment of the present invention has been described above, the present invention is not limited to this example. It is obvious to those skilled in the art that various modifications or modifications can be conceived within the scope of the technical idea described in the claims, and of course, the technical scope of the present invention is also applicable to them. Understood to belong to.

本発明に係る焼却処理方法は、処理室の出入口を閉じた状態で焼却処理を行う焼却炉(以下、密閉型焼却炉と呼ぶ)において特に好適に利用することができる。なぜなら、上記実施形態のような密閉型焼却炉においては、焼却処理の対象物の搬入および搬出が断続的となるために、処理効率を高めるには一度にできるだけ大量に焼却処理の対象物を搬入する必要があり、可燃物が一度に大量に燃焼する問題が生じやすいためである。上記実施形態のPCBを含有する廃棄物の焼却炉は、密閉型焼却炉の典型例である。 INDUSTRIAL APPLICABILITY The incineration treatment method according to the present invention can be particularly suitably used in an incinerator that performs incineration treatment with a door of a processing chamber being closed (hereinafter referred to as a closed incinerator). This is because, in the closed type incinerator as in the above-described embodiment, since the target of the incineration process is intermittently loaded and unloaded, in order to improve the processing efficiency, the target of the incineration process is loaded as much as possible at one time. This is because the combustible material is likely to burn in large quantities at once. The waste incinerator containing the PCB of the above embodiment is a typical example of a closed incinerator.

本発明に係る焼却処理方法でコンデンサ素子の焼却処理を実施した。まず、200リットルの上部が開放されたドラム缶3本にコンデンサ素子を40kgずつ収容し、3本のうちの2本のドラム缶に沸騰性液体として水を入れた。続いて、3本のドラム缶内の水の量を0リットル、20リットル、40リットルである状態で各ドラム缶を1台の台車にまとめて載せた。その後、ドラム缶を載せた台車を焼却炉内に搬入して廃棄物の焼却処理を実施した。なお、コンデンサ素子は、可燃物であるPCB含有油を含浸した絶縁紙とアルミ箔とを重ね合わせたものをロール巻きにしてパッケージ内に封入した構成となっている。 The capacitor element was incinerated by the incineration method according to the present invention. First, 40 kg of the capacitor element was accommodated in three drums of 200 liters each having an open upper part, and water was added as a boiling liquid to two of the three drums. Subsequently, the drums were placed on one trolley together with the amounts of water in the three drums being 0 liter, 20 liter, and 40 liter. After that, the truck carrying the drums was carried into the incinerator to incinerate the waste. The capacitor element has a structure in which insulating paper impregnated with PCB-containing oil, which is a combustible material, and aluminum foil are superposed and wound in a roll and enclosed in a package.

ドラム缶を炉内に搬入した後、焼却処理中の炉内温度を測定したところ、間隔を空けて計3回の急激な温度上昇が見られ、ドラム缶ごとに異なるタイミングで燃焼のピークを迎えたことが確認された。温度上昇時の炉内温度の最高値は、3回の温度上昇時ともに炉の許容温度上限である970℃以下であった。また、排ガス処理後のCO濃度を測定したところ、排出基準である100ppm未満のCO濃度となっていた。 When the temperature inside the furnace during the incineration process was measured after the drums were carried into the furnace, a rapid temperature increase was observed three times at intervals, and the combustion peak reached at different timing for each drum. Was confirmed. The maximum value of the temperature inside the furnace when the temperature was raised was 970° C. or lower, which is the upper limit of the allowable temperature of the furnace, when the temperature was raised three times. Moreover, when the CO concentration after the exhaust gas treatment was measured, the CO concentration was less than 100 ppm, which is the emission standard.

本実施例からも示されるように、本発明に係る廃棄物の焼却処理方法によれば、廃棄物の燃焼ピークをずらすことが可能となり、廃棄物の過剰燃焼に起因する炉材の劣化やCO濃度の上昇を抑えることができる。 As also shown in this example, according to the waste incineration method of the present invention, it is possible to shift the combustion peak of the waste, which causes deterioration of the furnace material and CO due to excessive combustion of the waste. An increase in concentration can be suppressed.

本発明は、PCB含有廃棄物の焼却処理に適用することができる。 INDUSTRIAL APPLICABILITY The present invention can be applied to incineration treatment of PCB-containing waste.

2 台車
3 ドラム缶
3a 第1のドラム缶
3b 第2のドラム缶
3c 第3のドラム缶
10 焼却炉
11 搬入待機室
12 処理室
12a 昇温部
12b 温度保持部
12c 冷却部
13 搬出待機室
14 扉
15 排気管
U 焼却対象単位
W 廃棄物
第1の廃棄物
第2の廃棄物
第3の廃棄物
2 dolly 3 drum can 3a first drum 3b second drum 3c third drum 10 incinerator 11 loading standby chamber 12 processing chamber 12a temperature raising part 12b temperature holding part 12c cooling part 13 unloading standby chamber 14 door 15 exhaust pipe U Unit to be incinerated W Waste W 1 First waste W 2 Second waste W 3 Third waste

Claims (4)

可燃物を含む廃棄物の焼却処理方法であって、
貯液性を有し、かつ開口部を有した、複数の収容領域それぞれに該廃棄物が収容され、
かつ各収容領域内の沸騰性液体の量がそれぞれ異なる状態となるように前記沸騰性液体が前記収容領域に入れられることで構成される焼却対象単位を焼却炉に搬入し、
前記廃棄物の焼却処理を行う、廃棄物の焼却処理方法。
A method for incinerating waste containing combustible materials,
The waste is stored in each of a plurality of storage areas having a liquid storage property and having an opening,
And the amount of the boiling liquid in each storage area is carried into the incinerator the incineration target unit constituted by being put in the storage area so that the boiling liquid is in a different state,
A method for incineration of waste, comprising incineration of the waste.
各収容領域は上部が開放された複数の容器内の領域である、請求項1に記載された廃棄物の焼却処理方法。 The waste incineration method according to claim 1, wherein each of the storage areas is an area in a plurality of containers having an open top. 前記収容領域に収容された前記廃棄物の搬送に台車を用いる、請求項1又は2に記載された廃棄物の焼却処理方法。 The waste incineration method according to claim 1 or 2, wherein a carriage is used to convey the waste stored in the storage area. 前記廃棄物がPCBを含む廃棄物である、請求項1〜3のいずれか一項に記載された廃棄物の焼却処理方法。 The incineration method for waste according to any one of claims 1 to 3, wherein the waste is a waste containing PCB.
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