JPS6363878B2 - - Google Patents
Info
- Publication number
- JPS6363878B2 JPS6363878B2 JP8650580A JP8650580A JPS6363878B2 JP S6363878 B2 JPS6363878 B2 JP S6363878B2 JP 8650580 A JP8650580 A JP 8650580A JP 8650580 A JP8650580 A JP 8650580A JP S6363878 B2 JPS6363878 B2 JP S6363878B2
- Authority
- JP
- Japan
- Prior art keywords
- waste
- crushed
- incinerator
- pellets
- radioactive
- 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
Links
- 239000002699 waste material Substances 0.000 claims description 21
- 238000000034 method Methods 0.000 claims description 19
- 239000008188 pellet Substances 0.000 claims description 13
- 230000002285 radioactive effect Effects 0.000 claims description 10
- 239000010849 combustible waste Substances 0.000 claims description 6
- 239000007787 solid Substances 0.000 description 9
- 238000009841 combustion method Methods 0.000 description 7
- 239000000463 material Substances 0.000 description 7
- 238000000748 compression moulding Methods 0.000 description 6
- -1 polyethylene Polymers 0.000 description 6
- 239000004698 Polyethylene Substances 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 5
- 239000004744 fabric Substances 0.000 description 5
- 229920000573 polyethylene Polymers 0.000 description 5
- 239000010893 paper waste Substances 0.000 description 4
- 230000006835 compression Effects 0.000 description 3
- 238000007906 compression Methods 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 238000003672 processing method Methods 0.000 description 3
- 239000002901 radioactive waste Substances 0.000 description 3
- 238000004378 air conditioning Methods 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000007689 inspection Methods 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 229920000742 Cotton Polymers 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000012857 radioactive material Substances 0.000 description 1
- 238000012857 repacking Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Description
【発明の詳細な説明】
本発明は原子力設備で発生する放射性雑可燃廃
棄物の減容処理方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for reducing the volume of radioactive miscellaneous combustible waste generated in nuclear facilities.
原子力発電所などの原子力設備では可燃性雑固
体廃棄物が多量に発生している。定期検査時の発
生量は特に多く、年間発生量は1000MWeツイン
ユニツトの軽水炉型原子力発電所で200ドラム
缶で1000本程度に達している。国内では、ごく最
近まで、これら廃棄物はそのままドラム缶詰めさ
れサイト内に保管貯蔵されてきた。しかし乍ら、
ドラム缶の発生本数が多く、スペース的に、サイ
ト内に保管貯蔵しきれなくなる時期が予想外に早
く到来することが明らかとなり、減容比が約80と
大きくとれる焼却処理が有望と判断されるに至
り、実際にこれら可燃性雑固体の焼却処理が行な
われ始めている。 Nuclear equipment such as nuclear power plants generate large amounts of combustible miscellaneous solid waste. The amount generated during periodic inspections is particularly large, and the annual amount generated reaches about 1,000 drums (200 drums) at a 1,000 MWe twin unit light water reactor nuclear power plant. In Japan, until recently, this waste has been canned in drums and stored on-site. However,
Due to the large number of drums generated, it became clear that the time would come sooner than expected when they would no longer be able to store them on-site due to space constraints, and incineration treatment with a large volume reduction ratio of approximately 80 was judged to be promising. As a result, incineration of these flammable miscellaneous solids has actually begun.
現在、焼却処理が可能と考えられている放射性
可燃性雑固体には紙、紙ウエス、衣類、布ウエ
ス、ポリエチレン、木材、可燃性空調用フイルタ
等がある。 Currently, radioactive combustible miscellaneous solids that are considered to be incinerated include paper, paper waste, clothing, cloth waste, polyethylene, wood, and flammable air conditioning filters.
これらの中、木材は定期検査時などに足場とし
て用いられるものが殆んどであるが、最近は金属
製のものに取つて代られ、その発生は稀れであ
る。また、可燃性空調用フイルタは最近開発が進
んできたものであつて採用している施設数も少な
くまた試験的な焼却処理にとどまつている。従つ
て、現在、放射線取扱い施設で発生している可燃
性雑固体のドラム缶数を減少させるには紙、紙ウ
エス、衣類、布ウエス、ポリエチレンを焼却減容
処理すれば効果的であることが判る。 Among these, wood is mostly used as scaffolding during periodic inspections, but recently metal has been replaced, and this occurrence is rare. Furthermore, although flammable air conditioning filters have recently been developed, the number of facilities that have adopted them is small, and the incineration process is still on a trial basis. Therefore, it is found that in order to reduce the number of drums of flammable miscellaneous solids currently generated in radiation handling facilities, it is effective to reduce the volume by incinerating paper, paper waste, clothing, cloth waste, and polyethylene. .
これらの可燃性雑固体は都市ゴミにも含まれ、
都市ゴミ成分の中でも比較的焼却処理を行ない易
い部類に属するため、都市ゴミ焼却施設として利
用されている方式に放射線防護の立場から若干の
改良を加えたものを、放射性可燃性雑固体焼却施
設に流用しているのが実情である。従つて、放射
性可燃性雑固体の焼却炉への供給方式も都市ゴミ
に対する。それと本質的には何ら変つていない。 These flammable miscellaneous solids are also included in municipal waste.
As it belongs to a category of municipal waste that is relatively easy to incinerate, we have developed a radioactive combustible miscellaneous solids incinerator using the method used in municipal waste incineration facilities with some improvements from the standpoint of radiation protection. The reality is that it is being misappropriated. Therefore, the method of supplying radioactive combustible miscellaneous solids to the incinerator is also similar to municipal waste. Essentially nothing has changed.
焼却処理方式には床燃焼方式、火格子燃焼方
式、充填層燃焼方式、移動床燃焼方式、移動火格
子燃焼方式、ロータリーキルン燃焼方式、流動層
燃焼方式など種々の方式があるが、被焼却物の供
給方法は大きく回分式と連続式のふたつに分ける
ことができる。焼却炉の安定運転の観点からは、
連続式の方が優れているが従来のものには各々下
記に述べる欠点があり、放射性廃棄物処理への適
用には十分なものとは云い難い。 There are various incineration methods such as bed combustion method, grate combustion method, packed bed combustion method, moving bed combustion method, moving grate combustion method, rotary kiln combustion method, and fluidized bed combustion method. Supply methods can be broadly divided into two types: batch type and continuous type. From the perspective of stable operation of the incinerator,
Although the continuous type is superior, each of the conventional types has the drawbacks described below, and it is difficult to say that they are sufficient for application to radioactive waste treatment.
第1図に示す従来の回分方式では、放射性物質
取扱い施設で発生する可燃性雑固体は通常、ポリ
エチレン袋に詰められた状態で廃棄物置場1に収
集される。これを人手で開袋し不燃物を分別し、
適当量を小さな袋に詰めかえた上で、焼却炉2の
炉頂より間欠的に投入する。これには次の欠点が
ある。 In the conventional batch system shown in FIG. 1, combustible miscellaneous solids generated in facilities handling radioactive materials are usually collected in a waste storage site 1 in a state packed in polyethylene bags. The bags are opened manually and the non-combustibles are separated.
After repacking the appropriate amount into a small bag, it is intermittently poured into the incinerator 2 from the top. This has the following drawbacks.
(イ) 全て人手作業であり、多大の労力を要する
上、被曝量の増大をまねく。(b) All work is done manually, requiring a great deal of labor and leading to an increase in radiation exposure.
(ロ) 間欠投入のため、炉内における被焼物量、炉
温、熱負荷、燃焼ガス量、燃焼状態などが変動
し、不完全燃焼を起こしやすい。(b) Due to intermittent feeding, the amount of material to be burned in the furnace, furnace temperature, heat load, amount of combustion gas, combustion conditions, etc. fluctuate, which tends to cause incomplete combustion.
(ハ) またこのために、燃焼状態の監視を行ないな
がら供給を調節する必要があるが、これらの自
動化は困難である。(c) For this purpose, it is necessary to adjust the supply while monitoring the combustion state, but it is difficult to automate this process.
(ニ) 不完全燃焼に伴ない、減容化が減少し、また
排ガスの後処理が面倒となる。(d) Due to incomplete combustion, volume reduction is reduced and exhaust gas after-treatment becomes troublesome.
(ホ) 廃棄物を破砕せずに分別しているため精度よ
い分別が困難であり、不燃物が混入しやすくト
ラブルの一因となる。(e) Since waste is separated without being crushed, accurate separation is difficult, and non-combustible materials are likely to get mixed in, causing problems.
また第2図に示す従来の連続方式では、廃棄物
仮置場の袋詰の廃棄物をそのまま破砕機3で破砕
し、貯留ホツパ4に一旦入れ、ここから焼却炉2
の供給ホツパ5に導き、この供給ホツパ5の底部
の供給フイーダ6により焼却炉2に連続的に供給
する。このように破砕を行なえば、金属類などの
分別回収が比較的簡単であると云うメリツトはあ
るが従来の方式には次の欠点がある。 In addition, in the conventional continuous system shown in Fig. 2, bagged waste at a temporary waste storage site is crushed as is in a crusher 3, placed in a storage hopper 4, and then transported to an incinerator 2.
, and is continuously fed to the incinerator 2 by a feeder 6 at the bottom of the feed hopper 5 . Although this method of crushing has the advantage that it is relatively easy to separate and recover metals, etc., the conventional method has the following drawbacks.
(イ) 放射性取扱い施設で処理すべき可燃性雑固体
量は都市ゴミ焼却炉でのそれに比較し、非常に
少ない。このため、供給量が非常に少なくな
り、破砕したままの状態では次のような問題点
があり、これらの解決が必要である。(b) The amount of combustible miscellaneous solids that must be treated in radioactive handling facilities is extremely small compared to that in municipal waste incinerators. For this reason, the supply amount becomes very small, and the following problems arise in the crushed state, and it is necessary to solve these problems.
(i) 乾燥した布などは破砕後非常に小さい見掛
け密度をもつため、定量取出しが非常に困難
であり、また容器内でもブリツジを作りやす
い。 (i) Dry cloth has a very small apparent density after being crushed, so it is very difficult to take out a quantitative amount, and it is easy to form brittleness even in a container.
(ii) 湿潤紙ウエスなどは器壁などに付着しやす
く、これまた定量切出しが困難であり、かつ
搬送も困難である。 (ii) Wet paper rags tend to adhere to the vessel walls, etc., making it difficult to cut out a fixed amount and also difficult to transport.
(ロ) 破砕により生じた、微粉あるいは綿ボコリの
ようなものは、気流に乗り焼却されずに、炉外
へ搬出される危険性が多い。(b) There is a high risk that fine powder or cotton lint produced by crushing will be carried out of the furnace without being incinerated by air currents.
上述のように従来放射性廃棄物取扱い施設で発
生する可燃性雑固体を連続焼却処理する場合、そ
の処理量(つまり焼却炉への供給量)が非常に少
なく、満足の得られる定量切り出し機および搬送
方法がなかつた。これを達成できれば放射性廃棄
物の焼却処理に適したすなわち信頼性の高いかつ
安定した運転が可能な焼却処理が出来る。 As mentioned above, when continuously incinerating combustible miscellaneous solids generated in conventional radioactive waste handling facilities, the amount to be processed (that is, the amount supplied to the incinerator) is very small, and a satisfactory quantitative cutting machine and transport method are required. There was no way. If this can be achieved, an incineration process suitable for incinerating radioactive waste, that is, capable of highly reliable and stable operation, will be possible.
本発明はこの問題を満足せしめる処理方法を提
供することを目的とするものである。 The object of the present invention is to provide a processing method that satisfies this problem.
すなわち本発明は、放射性可燃廃棄物を破砕機
にかけて破砕し、このように破砕した廃棄物を圧
縮機により圧縮してペレツト状とし、このように
圧縮形成した廃棄物ペレツトを焼却炉に連続的に
送給して焼却し減容化することを特徴とする、放
射性雑可燃廃棄物の処理方法にある。 That is, the present invention crushes radioactive combustible waste using a crusher, compresses the crushed waste using a compressor to form pellets, and continuously feeds the compressed waste pellets into an incinerator. A method for disposing radioactive miscellaneous combustible waste, which is characterized by transporting and incinerating it to reduce its volume.
以下本発明を添付図面第3図以下に例示したそ
の好適な実施例について詳述する。 DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will now be described in detail with reference to preferred embodiments illustrated in FIG. 3 of the accompanying drawings.
第3図に示す本発明の1実施例によれば、廃棄
物仮置場1のポリエチレン袋に詰められた放射性
雑可燃廃棄物、たとえば紙、紙ウエス、衣類、布
ウエスなどは袋詰のまま破砕機3にかけられて破
砕される。このようにして破砕された廃棄物は次
いで分別され金属などの不純物を取除いた後圧縮
成形機7に投入され、ペレツト状に圧縮成形され
る。 According to one embodiment of the present invention shown in FIG. 3, radioactive miscellaneous combustible waste packed in polyethylene bags in the temporary waste storage site 1, such as paper, paper waste, clothing, cloth waste, etc., is shredded while still being packed in the bag. It is crushed by machine 3. The thus crushed waste is then separated, and after removing impurities such as metals, it is fed into a compression molding machine 7 and compression molded into pellets.
この圧縮成形機7としては第4図に示すピスト
ンによる圧縮成形機が好適である。すなわち軸1
1を中心として回転する円板12に穿設したシリ
ンダ孔8に破砕廃棄物を入れ、ピストン9でこれ
を圧縮成形してペレツト10とするのである。 As this compression molding machine 7, a piston compression molding machine shown in FIG. 4 is suitable. i.e. axis 1
The crushed waste is put into a cylinder hole 8 formed in a disk 12 which rotates about 1, and is compressed and formed into pellets 10 by a piston 9.
このようなピストン方式が最も簡単な方法であ
るが、圧縮手段はこれに限らず、たとえばエクス
トルーダ等の押出機で紐状に圧縮成形したあと適
当な寸法に切断してペレツトとすることも可能で
ある。 This piston method is the simplest method, but the compression method is not limited to this.For example, it is also possible to compression mold the pellets into strings using an extruder or other extruder, and then cut them into appropriate sizes to make pellets. be.
このように圧縮成形したペレツトはホツパ5に
導かれ、ここから供給フイーダ6により焼却炉2
に連続的に供給されて焼却減容化されるのであ
る。 The pellets compressed in this way are led to a hopper 5, and from there are transported to an incinerator 2 by a feeder 6.
It is continuously supplied to the factory and incinerated to reduce its volume.
本発明方法によれば次のような効果が奏し得
る。 According to the method of the present invention, the following effects can be achieved.
(1) 破砕物を圧縮しペレツト状とすることにより
減容が図られ、貯留及び供給ホツパを小形化す
ることができる。場合により第3図に示すよう
に一方のホツパを省略することができる。(1) By compressing the crushed material into pellets, the volume can be reduced, and the storage and supply hoppers can be made smaller. In some cases, one of the hoppers can be omitted as shown in FIG.
(2) 破砕物は見掛密度が非常に小さく、これのハ
ンドリングに難があつたが、圧縮成形すること
によりハンドリング性が飛躍的に向上する。(2) The apparent density of the crushed material was very low, making it difficult to handle it, but compression molding dramatically improves handling properties.
(3) またこれと関連し通常のスクリユーフイー
ダ、空気輸送等により焼却炉への定量供給が可
能となり炉の安定運転に大きく寄与する。(3) Related to this, it is possible to supply a fixed amount to the incinerator using a regular screw feeder, pneumatic transport, etc., which greatly contributes to the stable operation of the incinerator.
本発明方法の実験例を示すと次のとおりであ
る。 Experimental examples of the method of the present invention are shown below.
紙、紙ウエス、衣類、布ウエスポリエチレンシ
ートなどをカツターミル式破砕機で10〜30mmに破
砕し、これを油圧プレスにより100Kg/cm2の圧力
でφ(直径)20mm×t(長さ)5mmの大きさの円柱
形ペレツトに成形した。 Paper, paper waste, clothing, cloth waste polyethylene sheets, etc. are crushed into 10 to 30 mm pieces using a cutter mill type crusher, and then crushed into φ (diameter) 20 mm x t (length) 5 mm pieces using a hydraulic press at a pressure of 100 kg/ cm2 . It was formed into cylindrical pellets of the same size.
上記の結果、破砕物の物性は下記の通り改善さ
れた。 As a result of the above, the physical properties of the crushed material were improved as shown below.
Γ見掛け密度 0.001〜0.1g/cm3⇒0.4〜0.9g/
cm3
Γ含水率 30%以上⇒約10%
上記操作で得られたペレツトを焼却処理に供し
たところ下記効果が認められた。Γ Apparent density 0.001~0.1g/cm 3 ⇒0.4~0.9g/
cm 3 Γ Moisture content 30% or more⇒approximately 10% When the pellets obtained by the above operation were subjected to incineration treatment, the following effects were observed.
(1) 一般に用いられているロータリーフイーダ、
スクリユーフイーダにより容易に定量切り出し
が可能となつた。またハンドリング性が飛躍的
に改善された。(1) Commonly used rotary leaf feeder,
The screw feeder allows easy quantitative cutting. Handling has also been dramatically improved.
(2) 破砕物ホツパ内でのブリツジの形成がなくな
つた。(2) Bridge formation within the crushed material hopper has disappeared.
(3) 被焼却物が炉内で気流に運ばれ不燃状態で炉
外へ排出されるという不具合が全くなくなつ
た。(3) The problem of incinerated materials being carried by the air current inside the furnace and being discharged outside the furnace in a non-flammable state has been completely eliminated.
(4) 炉内の燃焼状態は非常に安定し、運転制御性
が向上した。(4) The combustion conditions inside the furnace were extremely stable, and operational controllability was improved.
第1図は従来の回分式処理方法を説明する立面
図、第2図は従来の連続式処理方法を説明する立
面図、第3図は本発明方法を説明する立面図、第
4図は本発明方法に使用する圧縮成形機の1例の
立面図である。
1……廃棄物仮置場、2……焼却炉、3……破
砕機、4……貯留ホツパ、5……供給ホツパ、6
……供給フイーダ、7……圧縮成形機、8……シ
リンダ孔、9……ピストン、10……ペレツト、
11……軸、12……円板。
FIG. 1 is an elevational view explaining the conventional batch-type processing method, FIG. 2 is an elevational view explaining the conventional continuous-type processing method, FIG. 3 is an elevational view explaining the method of the present invention, and FIG. The figure is an elevational view of one example of a compression molding machine used in the method of the present invention. 1... Temporary waste storage site, 2... Incinerator, 3... Shredding machine, 4... Storage hopper, 5... Supply hopper, 6
... Supply feeder, 7 ... Compression molding machine, 8 ... Cylinder hole, 9 ... Piston, 10 ... Pellet,
11...axis, 12...disk.
Claims (1)
し、このように破砕した廃棄物を圧縮機により圧
縮してペレツト状とし、このようにして圧縮形成
した廃棄物ペレツトを焼却炉に連続的に送給して
焼却し減容化することを特徴とする、放射性雑可
燃廃棄物の処理方法。1 Radioactive miscellaneous combustible waste is crushed using a crusher, the crushed waste is compressed into pellets using a compressor, and the waste pellets thus compressed and formed are continuously sent to an incinerator. A method for disposing radioactive miscellaneous combustible waste, which is characterized by incinerating it and reducing its volume.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP8650580A JPS5712400A (en) | 1980-06-27 | 1980-06-27 | Method of treating radioactive non-fecal combustible waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP8650580A JPS5712400A (en) | 1980-06-27 | 1980-06-27 | Method of treating radioactive non-fecal combustible waste |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5712400A JPS5712400A (en) | 1982-01-22 |
| JPS6363878B2 true JPS6363878B2 (en) | 1988-12-08 |
Family
ID=13888832
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP8650580A Granted JPS5712400A (en) | 1980-06-27 | 1980-06-27 | Method of treating radioactive non-fecal combustible waste |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5712400A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0458777U (en) * | 1990-09-26 | 1992-05-20 |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60125600A (en) * | 1983-12-09 | 1985-07-04 | 株式会社日立製作所 | Method and device for treating spent ion exchange resin |
-
1980
- 1980-06-27 JP JP8650580A patent/JPS5712400A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0458777U (en) * | 1990-09-26 | 1992-05-20 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5712400A (en) | 1982-01-22 |
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