JPH04260407A - Waste gas treatment device and filter for use therein - Google Patents
Waste gas treatment device and filter for use thereinInfo
- Publication number
- JPH04260407A JPH04260407A JP3021735A JP2173591A JPH04260407A JP H04260407 A JPH04260407 A JP H04260407A JP 3021735 A JP3021735 A JP 3021735A JP 2173591 A JP2173591 A JP 2173591A JP H04260407 A JPH04260407 A JP H04260407A
- Authority
- JP
- Japan
- Prior art keywords
- filter
- exhaust gas
- treatment device
- gas treatment
- fibers
- 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
- 239000002912 waste gas Substances 0.000 title abstract 4
- 239000004745 nonwoven fabric Substances 0.000 claims abstract description 13
- 238000004381 surface treatment Methods 0.000 claims abstract description 5
- 239000000835 fiber Substances 0.000 claims description 19
- 239000003365 glass fiber Substances 0.000 claims description 7
- 239000004744 fabric Substances 0.000 claims description 3
- 239000002699 waste material Substances 0.000 abstract description 4
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 39
- 150000002013 dioxins Chemical class 0.000 description 15
- 239000010419 fine particle Substances 0.000 description 9
- 239000002245 particle Substances 0.000 description 7
- 238000011001 backwashing Methods 0.000 description 5
- 239000012717 electrostatic precipitator Substances 0.000 description 5
- 239000012784 inorganic fiber Substances 0.000 description 5
- 239000000428 dust Substances 0.000 description 4
- 230000002093 peripheral effect Effects 0.000 description 4
- 239000012716 precipitator Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 150000001805 chlorine compounds Chemical class 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 229920000049 Carbon (fiber) Polymers 0.000 description 2
- 229920002978 Vinylon Polymers 0.000 description 2
- 238000003915 air pollution Methods 0.000 description 2
- 239000004917 carbon fiber Substances 0.000 description 2
- 230000002542 deteriorative effect Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- TXCDCPKCNAJMEE-UHFFFAOYSA-N dibenzofuran Chemical compound C1=CC=C2C3=CC=CC=C3OC2=C1 TXCDCPKCNAJMEE-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 229920000728 polyester Polymers 0.000 description 2
- 230000001105 regulatory effect Effects 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 238000009423 ventilation Methods 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 1
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 150000004827 dibenzo-1,4-dioxins Chemical class 0.000 description 1
- 150000004826 dibenzofurans Chemical class 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000008267 milk Substances 0.000 description 1
- 210000004080 milk Anatomy 0.000 description 1
- 235000013336 milk Nutrition 0.000 description 1
- 229910017464 nitrogen compound Inorganic materials 0.000 description 1
- 150000002830 nitrogen compounds Chemical class 0.000 description 1
- NFBOHOGPQUYFRF-UHFFFAOYSA-N oxanthrene Chemical compound C1=CC=C2OC3=CC=CC=C3OC2=C1 NFBOHOGPQUYFRF-UHFFFAOYSA-N 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- -1 that is Substances 0.000 description 1
- 239000002759 woven fabric Substances 0.000 description 1
Landscapes
- Filtering Materials (AREA)
- Filtering Of Dispersed Particles In Gases (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、排ガス処理装置、特に
焼却炉の排ガスに含まれる微粒子の除去に好適な排ガス
処理装置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas treatment device, and particularly to an exhaust gas treatment device suitable for removing particulates contained in the exhaust gas of an incinerator.
【0002】0002
【従来の技術】事業所や家庭などから排出された廃棄物
を焼却する焼却炉の排ガスには、塩素化合物、窒素化合
物、硫黄化合物、煤塵などの有害物質が含まれており、
これらをそのまま大気中に放出すると深刻な大気汚染を
引き起こす原因となる。特に、塩素化合物中には、ポリ
塩化ジベンゾ−p−ダイオキシン(Polychlor
inated dibenzo−p−dioxin;P
CDDs)、ポリ塩化ジベンゾフラン(Polychl
orinated dibenzofuran;PDD
Fs)、コプレーナ(Coplanar)PCBなど、
極めて強い毒性を有するダイオキシン関連物質(以下、
ダイオキシン類という)が含まれているので、これらを
効率的に除去することが大気汚染を防止する上で重要な
課題となる。[Prior Art] The exhaust gas from incinerators that incinerate waste discharged from businesses and households contains harmful substances such as chlorine compounds, nitrogen compounds, sulfur compounds, and soot.
If these are released into the atmosphere as they are, they will cause serious air pollution. In particular, among chlorine compounds, polychlorinated dibenzo-p-dioxin (Polychlor
inated dibenzo-p-dioxin;P
CDDs), polychlorinated dibenzofurans (Polychl
orinated dibenzofuran;PDD
Fs), Coplanar PCB, etc.
Dioxin-related substances (hereinafter referred to as
They contain dioxins (dioxins), so the efficient removal of these is an important issue in preventing air pollution.
【0003】従来、焼却炉の排ガスに含まれるダイオキ
シン類の規制値としては、「廃棄物処理に係るダイオキ
シン等専門家会議」(昭和59年5月)の報告書におい
て、0.5ng/m3 Nとすべきことが提案され、平
成2年12月に定められた「ダイオキシン類発生防止等
ガイドライン」(厚生省水道環境部環境整備課)におい
てもこの値が採用されている。しかし、欧米諸国では上
記規制値を0.1ng/m3 Nとしている例が多く、
日本でもこの規制値を欧米並に引き上げるべきであると
する意見が強いことから、将来的には規制値引き上げの
方向に向かうものと考えられる。Conventionally, the regulation value for dioxins contained in incinerator exhaust gas was set at 0.5 ng/m3N in the report of the ``Dioxins, etc. Expert Committee on Waste Treatment'' (May 1981). This value was also adopted in the ``Guidelines for Prevention of Dioxins'' established in December 1990 (Environmental Development Division, Water Supply and Environment Department, Ministry of Health and Welfare). However, in many European and American countries, the above regulation value is set at 0.1ng/m3N,
In Japan, there is a strong opinion that this regulatory value should be raised to the same level as in Europe and the United States, so it is thought that the trend will be toward raising the regulatory value in the future.
【0004】0004
【発明が解決しようとする課題】現在、焼却炉の排ガス
に含まれるダイオキシン類を除去する装置としては、特
に新規なものがあるわけではなく、通常の排ガス処理用
集塵装置、すなわち電気集塵器やバグフィルタなどが利
用されている。また、前記ガイドラインにおいても、装
置として電気集塵器または濾過式集塵器を挙げており、
単にこれらの集塵器の入口の排ガス温度を極力低下する
よう勧告しているに過ぎない。[Problems to be Solved by the Invention] Currently, there are no particularly new devices for removing dioxins contained in the exhaust gas of incinerators, but there are conventional dust collectors for treating exhaust gas, that is, electrostatic precipitators. Containers and bag filters are used. In addition, the guidelines also mention electrostatic precipitators or filtration type precipitators as devices,
It merely recommends that the exhaust gas temperature at the inlet of these precipitators be reduced as much as possible.
【0005】ところが、上記電気集塵器やバグフィルタ
は、以下の理由により排ガス中のダイオキシン類を効率
的に除去することができないという問題がある。However, the electrostatic precipitator and bag filter described above have a problem in that they cannot efficiently remove dioxins from exhaust gas for the following reason.
【0006】まず、電気集塵器は、圧力損失が小さく、
かつ大容量のガス処理に適しているため、焼却炉の排ガ
ス処理に広く利用されているが、最近、通常実施されて
いる300℃付近の運転温度では、却って集塵器内でダ
イオキシン類が発生することが指摘され、各方面に衝撃
を与えている(「安全工学」27 No.6,(198
8)P336〜P343参照)。First, electrostatic precipitators have low pressure loss;
It is also suitable for large-capacity gas processing, so it is widely used for incinerator exhaust gas processing. However, recently, when the operating temperature is usually around 300°C, dioxins are generated inside the dust collector. It has been pointed out that the
8) See P336-P343).
【0007】これは、塩素化合物が反応してダイオキシ
ン類を生成するのに適した温度が300℃付近であり、
この付近の温度で排ガスが集塵器内に比較的長時間滞留
すること、これに加えて集塵器のコロナ放電が上記反応
を促進することなどが原因であると考えられる。従って
、ダイオキシン類の生成を抑制するためには、集塵器を
200℃以下の温度で運転することが有効であるとの提
案がなされている(前記文献)が、未だ実用化には至っ
ていない。[0007] This is because the suitable temperature for chlorine compounds to react and produce dioxins is around 300°C;
This is thought to be due to the fact that the exhaust gas remains in the precipitator for a relatively long time at a temperature around this temperature, and in addition to this, corona discharge in the precipitator accelerates the above reaction. Therefore, in order to suppress the production of dioxins, it has been proposed that it is effective to operate the dust collector at a temperature of 200 degrees Celsius or less (see the above document), but this has not yet been put to practical use. .
【0008】他方、バグフィルタはその基本的な性能と
して、サブミクロンオーダーの微粒子の捕集効率が悪く
( 0.3〜0.5μmの粒子の捕集効率は99%程度
)、ダイオキシン類は、0.5μm以下のフライアッシ
ュに吸着されている場合が多いので、バグフィルタによ
るダイオキシン類の効率的な除去は望めない。また、バ
グフィルタには、圧力損失が大きい(150〜250m
mAq)という欠点もある。On the other hand, the basic performance of bag filters is that they have poor collection efficiency for submicron-order fine particles (the collection efficiency for particles of 0.3 to 0.5 μm is about 99%), and that they have poor collection efficiency for dioxins. Since dioxins are often adsorbed by fly ash with a size of 0.5 μm or less, efficient removal of dioxins by bag filters cannot be expected. In addition, bag filters have a large pressure loss (150 to 250 m
There is also the drawback of mAq).
【0009】なお、サブミクロンオーダーの微粒子の捕
集に好適とされる装置として、HEPAフィルタ(Hi
gh Efficiency Particulate
Air Filter)が知られている。
ところが、通常のHEPAフィルタは、逆洗することが
できないので、使い捨てにならざるを得ず不経済である
こと、また、集塵効率を高め、かつ寿命を延ばすために
は、通風風速を0.5m/分程度にする必要があるが、
これは焼却炉の排ガス処理用としては濾過面積を非常に
大きく取ることになり、極めて大きな設置面積を必要と
することなど、多くの欠点があり、到底実用には供せら
れない。[0009] A HEPA filter (Hi
gh Efficiency Particulate
Air Filter) is known. However, since normal HEPA filters cannot be backwashed, they have to be disposable, which is uneconomical.Also, in order to increase dust collection efficiency and extend the lifespan, the ventilation speed must be set to 0. It is necessary to set the speed to about 5m/min,
This method requires a very large filtration area for treating exhaust gas from an incinerator, and has many drawbacks, such as requiring an extremely large installation area, and cannot be put to practical use.
【0010】本発明は、上記した問題点に着目してなさ
れたものであり、その目的は、焼却炉の排ガスに含まれ
るダイオキシン類を効率的に除去することのできる排ガ
ス処理装置を提供することにある。The present invention has been made in view of the above-mentioned problems, and its purpose is to provide an exhaust gas treatment device that can efficiently remove dioxins contained in the exhaust gas of an incinerator. It is in.
【0011】[0011]
【課題を解決するための手段】本発明者らは、逆洗が可
能なHEPAフィルタ(NASA〔米航空宇宙局〕規準
により、0.5μmの粒子に対してクラス50以下)を
開発するために鋭意研究を続けた結果、0.5μmまた
はそれ以下の繊維からなる不織布にフッ素樹脂の表面処
理を施したフィルタを用いることによって前記目的が達
成される、という知見を得た。[Means for Solving the Problems] In order to develop a backwashable HEPA filter (class 50 or less for particles of 0.5 μm according to NASA [National Aeronautics and Space Administration] standards) As a result of intensive research, we have found that the above objective can be achieved by using a filter made of a nonwoven fabric made of fibers of 0.5 μm or smaller and surface-treated with a fluororesin.
【0012】本発明者らは、先にフッ素樹脂の表面処理
を施した繊維からなる微粉捕集用HEPAフィルタを開
発した(特開昭63−111915号公報)が、本発明
のフィルタは、このHEPAフィルタに比べると、少な
くとも焼却炉の排ガスに含まれる微粒子の除去という点
では格段に優れた性能を備えている。これは、上記微粉
捕集用HEPAフィルタが実質的に編織布で構成されて
いるのに対し、本発明のフィルタは不織布で構成されて
おり、0.5μm以下の微粒子に関しては編織布よりも
不織布の方が捕集効率が良いためであると考えられる。The present inventors have previously developed a HEPA filter for collecting fine particles made of fibers that have been surface-treated with fluororesin (Japanese Patent Application Laid-Open No. 111915/1983). Compared to HEPA filters, it has significantly superior performance, at least in terms of removing particulates contained in incinerator exhaust gas. This is because, while the above-mentioned HEPA filter for collecting fine particles is substantially composed of a woven fabric, the filter of the present invention is composed of a non-woven fabric. This is thought to be because the collection efficiency is better.
【0013】本発明のフィルタに用いる不織布は、ガラ
ス繊維、炭素繊維などの無機繊維、ポリエステル繊維、
ビニロン繊維などの有機繊維のいずれもが使用可能であ
るが、耐熱性の点で無機繊維がより好ましく、さらに製
造原価を考慮すると無機繊維の中でもガラス繊維が特に
好ましい。本発明のフィルタは、サブミクロンオーダー
の微粒子、とりわけダイオキシン類などの有害物質が吸
着している0.5μm以下の微粒子の捕集を目的として
いるため、使用する繊維の直径は、0.5μmまたはそ
れ以下にする必要がある。The nonwoven fabric used in the filter of the present invention includes inorganic fibers such as glass fibers and carbon fibers, polyester fibers,
Although any organic fibers such as vinylon fibers can be used, inorganic fibers are more preferable in terms of heat resistance, and glass fibers are particularly preferable among inorganic fibers in view of manufacturing cost. The filter of the present invention is intended to collect submicron-order fine particles, especially fine particles of 0.5 μm or less to which harmful substances such as dioxins are adsorbed, so the diameter of the fibers used is 0.5 μm or less. It needs to be less than that.
【0014】本発明のフィルタは、不織布を構成する繊
維の表面にフッ素樹脂をコーティングしたことにより、
繊維の表面に微粒子が付着し難くなっているので、逆洗
時に微粒子を容易に剥落させることができる。フッ素樹
脂は、必ずしも繊維の一本一本に全てコーティングする
必要はなく、例えばフィルタを排ガス処理装置に装着し
た際に排ガスの流入側となる面にフッ素樹脂を含むエマ
ルジョンまたは溶液などを塗布する程度で充分である。
本発明のフィルタは、繊維の径、不織布の密度、フッ素
樹脂表面処理の程度によって微粒子の捕集効率が異なる
が、従来からある通常のHEPAフィルタに匹敵する性
能を得ることは困難ではなく、その場合も逆洗は可能で
ある。[0014] The filter of the present invention has a fluororesin coating on the surface of the fibers constituting the nonwoven fabric.
Since it is difficult for fine particles to adhere to the surface of the fibers, the fine particles can be easily peeled off during backwashing. It is not necessarily necessary to coat each and every fiber with fluororesin; for example, an emulsion or solution containing fluororesin may be applied to the side that will be the inlet side of the exhaust gas when the filter is installed in an exhaust gas treatment device. is sufficient. The filter of the present invention differs in particulate collection efficiency depending on the fiber diameter, the density of the nonwoven fabric, and the degree of fluororesin surface treatment, but it is not difficult to obtain performance comparable to conventional HEPA filters. Backwashing is also possible in this case.
【0015】このように、本発明のフィルタは、逆洗が
可能なため、微粒子の捕集性能が劣化することなく長期
間の使用に耐え、また通風風速を1〜2m/分程度と大
きくすることができるので、設置面積が狭くて済むなど
、経済的にも有利である。[0015] As described above, since the filter of the present invention can be backwashed, it can be used for a long period of time without deteriorating its particulate collection performance, and the ventilation speed can be increased to about 1 to 2 m/min. Therefore, it is economically advantageous, such as requiring only a small installation area.
【0016】本発明のフィルタの好ましい形状の一例を
図1および図2に示す。図2は、図1に示すフィルタの
部分拡大図である。このフィルタ1は、小さな体積で捕
集面積を大きくできるよう、全体が襞状に加工されてい
る。それぞれの襞の隙間には、金属、紙、合成樹脂など
からなる山形状のセパレータ2が介装され、フィルタ1
の変形を防いでいる。上記フィルタ1およびセパレータ
2は、枠体3に挿入された状態で排ガス処理装置に装着
される。図2の実線矢印で示すように、排ガスは、フィ
ルタ1の下方から上方に流れ、このときフィルタ1の下
面側に排ガス中の微粒子が捕集される。また、逆洗時に
は、同図の破線矢印で示すように、噴出気体をフィルタ
1の上方から下方に流し、その際のセパレータ2の振動
によって捕集された微粒子をフィルタ1から離脱させる
。An example of a preferred shape of the filter of the present invention is shown in FIGS. 1 and 2. FIG. 2 is a partially enlarged view of the filter shown in FIG. The entire filter 1 is processed into a pleated shape so that the collection area can be increased with a small volume. A mountain-shaped separator 2 made of metal, paper, synthetic resin, etc. is interposed in the gap between each fold, and the filter 1
prevents deformation. The filter 1 and separator 2 are inserted into the frame 3 and installed in an exhaust gas treatment device. As shown by the solid arrow in FIG. 2, the exhaust gas flows upward from the bottom of the filter 1, and at this time, particulates in the exhaust gas are collected on the lower surface side of the filter 1. Further, during backwashing, as shown by the broken line arrow in the figure, the ejected gas is caused to flow from above to below the filter 1, and the collected particles are separated from the filter 1 by the vibration of the separator 2 at that time.
【0017】図3は、フィルタ1の形状の他の例である
。このフィルタ1は、内外で折り返されて無端状に連続
する襞状に加工され、その内周面には、同様な形状を有
する多孔質のセパレータ2が装着されている。同図の実
線矢印で示すように、このフィルタ1は、その外周面側
からセパレータ2の内周面側に排ガスが流れ、フィルタ
1の外周面側に排ガス中の微粒子が捕集されるようにな
っている。また、逆洗時には、同図の破線矢印で示すよ
うに、噴出気体をフィルタ1の開口部4からセパレータ
2の内周面側を通じてフィルタ1の外周面側に流し、そ
の際のセパレータ2の振動によって捕集した微粒子をフ
ィルタ1から離脱させる。FIG. 3 shows another example of the shape of the filter 1. This filter 1 is folded inside and out to form an endless continuous pleat, and a porous separator 2 having a similar shape is attached to the inner peripheral surface of the filter 1. As shown by the solid arrow in the figure, this filter 1 is designed so that exhaust gas flows from its outer peripheral surface to the inner peripheral surface of the separator 2, and fine particles in the exhaust gas are collected on the outer peripheral surface of the filter 1. It has become. In addition, during backwashing, as shown by the broken line arrow in the figure, the ejected gas is caused to flow from the opening 4 of the filter 1 through the inner circumferential surface of the separator 2 to the outer circumferential surface of the filter 1, and the vibration of the separator 2 at this time is The collected particulates are removed from the filter 1.
【0018】本発明のフィルタは、厚手の不織布を用い
ることにより、単独でも充分な強度が得られるが、例え
ば図4に示すように、フッ素樹脂の表面処理を施した不
織布1aに繊維基布1bを積層して用いることにより、
強度、厚さおよび圧力損失の面で有利になる。繊維基布
1bとしては、不織布1aと同様、ガラス繊維、炭素繊
維などの無機繊維や、ポリエステル繊維、ビニロン繊維
などの有機繊維が使用可能であるが、耐熱性の点で無機
繊維、特にガラス繊維が好適である。The filter of the present invention can obtain sufficient strength even when used alone by using a thick non-woven fabric. For example, as shown in FIG. By stacking and using
Benefits in terms of strength, thickness and pressure drop. As the fiber base fabric 1b, inorganic fibers such as glass fibers and carbon fibers, and organic fibers such as polyester fibers and vinylon fibers can be used as in the nonwoven fabric 1a, but from the viewpoint of heat resistance, inorganic fibers, especially glass fibers is suitable.
【0019】本発明のフィルタを廃棄物焼却炉の排ガス
処理に適用する場合は、熱交換器や水の噴射など周知の
冷却手段を用いて、フィルタ通過時の排ガス温度をあら
かじめ250℃以下、より好ましくは200℃以下に冷
却しておく必要がある。また、排ガスに含まれる塩化水
素、硫黄酸化物などの有害な酸性物質を除去するため、
水の噴射に代えて石灰乳やアンモニア水を噴射するなど
、周知の排ガス処理法を併用することが望ましく、さら
に必要であれば、本発明のフィルタを取り付けた排ガス
処理装置の前段にサイクロン、バグフィルタ、電気集塵
器、スクラバなどを設置して微粒子を予備捕集してもよ
い。このような廃棄物焼却設備の一例を図5に示す。When the filter of the present invention is applied to the treatment of exhaust gas from a waste incinerator, the temperature of the exhaust gas as it passes through the filter is controlled in advance to 250°C or lower using a well-known cooling means such as a heat exchanger or water injection. Preferably, it is necessary to cool the temperature to 200°C or lower. In addition, in order to remove harmful acidic substances such as hydrogen chloride and sulfur oxides contained in exhaust gas,
It is desirable to use well-known exhaust gas treatment methods, such as injecting lime milk or aqueous ammonia instead of water injection, and if necessary, install a cyclone or bug in the front stage of the exhaust gas treatment equipment equipped with the filter of the present invention. Filters, electrostatic precipitators, scrubbers, etc. may be installed to pre-collect particulates. An example of such waste incineration equipment is shown in FIG.
【0020】[0020]
【実施例】直径約0.2μmのガラス繊維からなる不織
布にフッ素樹脂の表面処理を施して本発明フィルタを作
成した。また、比較例として直径2〜3μmのガラス繊
維からなる不織布にフッ素樹脂の表面処理を施して上記
フィルタと同一形状、同一寸法のフィルタを作成した。
次に、直径0.2〜5μmの炭酸カルシウム微粒子を5
mg/m3 N含有する気体を80℃、風速1m/分の
条件でそれぞれのフィルタに通した。フィルタを通過し
た微粒子の個数(個/10l)を粒径別に測定し、下記
の表1に示す結果を得た。EXAMPLE A filter of the present invention was prepared by surface-treating a nonwoven fabric made of glass fiber with a diameter of about 0.2 μm with a fluororesin. In addition, as a comparative example, a filter having the same shape and dimensions as the above filter was prepared by subjecting a nonwoven fabric made of glass fibers having a diameter of 2 to 3 μm to surface treatment with a fluororesin. Next, 5 pieces of calcium carbonate fine particles with a diameter of 0.2 to 5 μm were added.
A gas containing mg/m3N was passed through each filter under conditions of 80°C and a wind speed of 1 m/min. The number of particles (particles/10 liters) that passed through the filter was measured according to particle size, and the results shown in Table 1 below were obtained.
【0021】[0021]
【表1】[Table 1]
【0022】次に、上記と同様の条件で本発明フィルタ
と市販HEPAフィルタ(クラス100)との性能比較
を行い、図6に示す結果を得た。本発明フィルタは、1
時間毎に逆洗して付着微粒子を払い落としながら使用し
た。一方、市販HEPAフィルタは、逆洗不可能なため
、連続して使用した。Next, the performance of the filter of the present invention and a commercially available HEPA filter (class 100) was compared under the same conditions as above, and the results shown in FIG. 6 were obtained. The filter of the present invention has 1
It was used while backwashing every hour to shake off adhering particles. On the other hand, commercially available HEPA filters could not be backwashed, so they were used continuously.
【0023】図から明らかなように、市販HEPAフィ
ルタは、約4時間経過後、圧力損失が50mmAqを超
えた時点で破損してしまった。As is clear from the figure, the commercially available HEPA filter broke when the pressure loss exceeded 50 mmAq after about 4 hours.
【0024】[0024]
【発明の効果】本発明によれば、下記の効果を得ること
ができる。[Effects of the Invention] According to the present invention, the following effects can be obtained.
【0025】(1).本発明の排ガス処理装置用フィル
タは、焼却炉の排ガスに含まれる微粒子、特にダイオキ
シン類を含有する0.5μm以下の微粒子を効率的に除
去することができる。(1). The filter for an exhaust gas treatment device of the present invention can efficiently remove particulates contained in the exhaust gas of an incinerator, particularly particulates of 0.5 μm or less that contain dioxins.
【0026】(2).本発明のフィルタは、逆洗が可能
なため、微粒子の捕集性能が劣化することなく長期間の
繰り返し使用が可能である。(2). Since the filter of the present invention can be backwashed, it can be used repeatedly for a long period of time without deteriorating its particulate collection performance.
【0027】(3).本発明のフィルタは、通過風量が
大きいので、排ガス処理装置を小形化することができる
。(3). Since the filter of the present invention allows a large amount of air to pass through, it is possible to downsize the exhaust gas treatment device.
【図1】本発明の一実施例である排ガス処理装置用フィ
ルタを示す一部破断斜視図である。FIG. 1 is a partially cutaway perspective view showing a filter for an exhaust gas treatment device that is an embodiment of the present invention.
【図2】図1の部分拡大図である。FIG. 2 is a partially enlarged view of FIG. 1;
【図3】本発明の他の実施例である排ガス処理装置用フ
ィルタを示す斜視図である。FIG. 3 is a perspective view showing a filter for an exhaust gas treatment device according to another embodiment of the present invention.
【図4】本発明の排ガス処理装置用フィルタを示す要部
拡大断面図である。FIG. 4 is an enlarged sectional view of a main part of the filter for an exhaust gas treatment device of the present invention.
【図5】本発明の排ガス処理装置を組み込んだ廃棄物焼
却設備の全体構成図である。FIG. 5 is an overall configuration diagram of a waste incineration facility incorporating the exhaust gas treatment device of the present invention.
【図6】本発明の排ガス処理装置用フィルタと市販HE
PAフィルタの性能を比較するためのグラフ図である。[Figure 6] Filter for exhaust gas treatment equipment of the present invention and commercially available HE
It is a graph diagram for comparing the performance of PA filters.
1 フィルタ 1a 不織布 1b 繊維基布 2 セパレータ 3 枠体 4 開口部 1 Filter 1a Nonwoven fabric 1b Fiber base fabric 2 Separator 3 Frame 4 Opening
Claims (4)
.5μmまたはそれ以下の繊維からなる不織布を有する
フィルタを備えていることを特徴とする排ガス処理装置
。[Claim 1] Diameter 0 with fluororesin surface treatment
.. An exhaust gas treatment device comprising a filter having a nonwoven fabric made of fibers of 5 μm or less.
徴とする請求項1記載の排ガス処理装置。2. The exhaust gas treatment device according to claim 1, wherein the fibers are glass fibers.
.5μmまたはそれ以下の繊維からなる不織布を有する
ことを特徴とする排ガス処理装置用フィルタ。[Claim 3] Diameter 0 with fluororesin surface treatment
.. A filter for an exhaust gas treatment device, characterized by having a nonwoven fabric made of fibers of 5 μm or less.
とする請求項3記載の排ガス処理装置用フィルタ。4. The filter for an exhaust gas treatment device according to claim 3, wherein the fiber base fabric is laminated.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3021735A JPH04260407A (en) | 1991-02-15 | 1991-02-15 | Waste gas treatment device and filter for use therein |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3021735A JPH04260407A (en) | 1991-02-15 | 1991-02-15 | Waste gas treatment device and filter for use therein |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04260407A true JPH04260407A (en) | 1992-09-16 |
Family
ID=12063338
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3021735A Pending JPH04260407A (en) | 1991-02-15 | 1991-02-15 | Waste gas treatment device and filter for use therein |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04260407A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2001091883A1 (en) * | 2000-05-31 | 2001-12-06 | Miura Co., Ltd. | Filter for sampling chlorinated organic compound |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6139085B2 (en) * | 1976-04-27 | 1986-09-02 | Huyck Corp | |
JPS6290395A (en) * | 1985-06-24 | 1987-04-24 | ニッタ株式会社 | Filter paper and its production |
-
1991
- 1991-02-15 JP JP3021735A patent/JPH04260407A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6139085B2 (en) * | 1976-04-27 | 1986-09-02 | Huyck Corp | |
JPS6290395A (en) * | 1985-06-24 | 1987-04-24 | ニッタ株式会社 | Filter paper and its production |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2001091883A1 (en) * | 2000-05-31 | 2001-12-06 | Miura Co., Ltd. | Filter for sampling chlorinated organic compound |
US6890374B2 (en) | 2000-05-31 | 2005-05-10 | Miura Co., Ltd. | Filter for sampling chlorinated organic compound |
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