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JP4017252B2 - Flue gas treatment equipment in an incinerator - Google Patents
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JP4017252B2 - Flue gas treatment equipment in an incinerator - Google Patents

Flue gas treatment equipment in an incinerator Download PDF

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JP4017252B2
JP4017252B2 JP14126398A JP14126398A JP4017252B2 JP 4017252 B2 JP4017252 B2 JP 4017252B2 JP 14126398 A JP14126398 A JP 14126398A JP 14126398 A JP14126398 A JP 14126398A JP 4017252 B2 JP4017252 B2 JP 4017252B2
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incinerator
tube
port
jet
air
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JPH11337044A (en
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望月▲たく▼夫
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望月 ▲たく▼夫
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • Y02A50/2351Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust

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Description

【0001】
【産業上の利用分野】
本発明は、例えば焼却炉から放出される排煙中のミスト状の浮遊微粒子を捕捉する排煙処理装置に関するものである。
【0002】
【従来の技術】
焼却炉の煙は、焼却物が加熱や燃焼によりミスト状の微粒子として蒸散し、排気に混在したものであって、焼却物が合成樹脂等を含む場合、このミストの中には合成樹脂が加熱分解により、例えばダイオキシン等の有害物質の微粒子が多量に含まれる。
【0003】
このような焼却炉からの排煙中に含まれるダイオキシン等の有害物質の微粒子を捕捉する場合、例えば実開平1−69618号の第14図にも示されているようなフィルタ(所謂バグフィルタ)で濾過する濾過集塵装置が知られている。
【0004】
ところがこのバグフィルタ式の濾過集塵装置では、集塵率は高いものの、圧力損失が例えば100〜200mmAqと大きいうえ、捕捉できる粒度が一般的なものでは20〜 0.1μであり、特に 0.1μ以下の極微小なミスト状の粒子を捕捉する場合には装置が大型で、イニシャルコスト並びにランニングコストの高い電気集塵装置を用いなくては成らないと言う問題があった。
【0005】
そこで、特開平3−232514号の第2図に示すようなイニシャルコスト並びにランニングコストの安価なシャワーリング方式の洗浄塔(所謂ジェットスクラバー)が広く用いられている。
【0006】
【発明が解決しようとする課題】
ところが上記シャワーリング方式の洗浄塔では、極微小なミスト状の粒子を含んだ焼却炉からの排煙中に水をシャワー状に供給し、シャワーの水滴に処理気体中の極微小なミスト状の粒子を接触させて捕捉するもので、大量の水を必要とすると言う問題があった。
【0007】
更に、シャワー状に供給された水により排煙中の極微小なミスト状の粒子を接触させて捕捉する場合、特開平3−232514号の所謂ジェットスクラバーでは、シャワー状に噴射された水により処理気体に流れを生じさせるので処理気体との接触効率が悪く成ってしまうと言う問題があった。
また、静止している正圧乃至は常圧の排煙の中にシャワーの水滴を供給する場合には、その水滴は排煙中の微粒子を押し退けて飛翔するために微粒子とシャワーの水滴との接触効率が低い上、シャワー状の水滴の流走により煙にシャワーの流下方向に沿う流れが生じ易い。
【0008】
こうして処理気体にシャワーの流下方向に流れる流れが生じると、排煙中の微粒子がシャワーとともに流れる状態となり、排煙中の極微小なミスト状の粒子とシャワーの水滴との接触が良好に行われず、微粒子の捕捉効率が大幅に低下してしまうと言う問題もある。
また、焼却炉からの排煙中に含まれるダイオキシン等の有害物質の発生は、燃焼温度が800℃以下の時に発生し易いことから、燃焼温度は比較的高く設定される。
【0009】
この燃焼温度を高くするために燃焼口にブロアー等の送風装置を設け、この送風装置からの送風で炉内の燃焼を促進し、その燃焼温度を高く維持するようになっており、かかる送風装置のために焼却炉も大型化してしまう。
しかも、送風装置のモータ等の駆動に要する電力消費も大きく、その分ランニングコストも高くなってしまうだけでなく制御の手間もかかってしまう等の問題もあった。
【0010】
本発明は上記問題点に鑑み提案されたもので、焼却炉から排出される排煙中に含まれる有害物質等発生を可及的に少なくするとともに、発生した有害物質等の極微小なミスト状の粒子の発生を余すところ無く捕捉して環境汚染を無くせるようにした焼却炉における排煙処理装置を提供できるようにするとともに、焼却炉及び排煙処理装置をコンパクトに纏められるようにすることを目的とするものである。
【0011】
【課題を解決するための手段】
上記目的を達成するために本発明にかかる焼却炉における排煙処理装置は、焼却炉と焼却炉から排出される排煙中の浮遊微粒子を捕捉する浮遊微粒子捕捉装置とからなり、焼却炉は、送風または送風とともに燃料を供給する燃焼口と、燃焼排ガスを炉外に放出する排煙口とを有し、浮遊微粒子捕捉装置は、粒子捕捉用液体を貯溜した密閉可能な容器と、吐出口が密閉可能な容器に開口する微粒子捕捉管と、密閉可能な容器に貯溜された粒子捕捉用液体を加圧する加圧ポンプと、該加圧ポンプで加圧された圧力流体を微粒子捕捉管に噴射する噴射ノズルと、微粒子捕捉管と噴射ノズルとの間に形成された吸引室とを備えたジェットポンプを有し、該ジェットポンプの吸引室を焼却炉の排煙口と連通させ、噴射ノズルと微粒子捕捉管との間に外気吸引口を設けるとともに、密閉可能な容器の上部空間を燃焼口に連結させたことを特徴とするものである。
【0012】
また、微粒子捕捉管の吐出口から密閉可能な容器の上部空間を介して燃焼口に至る送風路中に密閉可能な容器の内圧調節手段を設けたり、ジェットポンプが、噴射ノズルの前方に保護管を設け、加圧された流体を噴射ノズルから保護管内に噴射して保護管内に負圧を形成し、当該保護管内に形成された負圧で空気を吸引して保護管内の流体を混気ジェット流にし、該混気ジェットジェット流を保護管から微粒子捕捉管に噴射して微粒子捕捉管内に負圧を形成する混気式ジェットポンプにしたことも特徴の1つである。
【0013】
【発明の実施の形態】
以下、本発明に係る焼却炉における排煙処理装置の実施の形態を図面に基づいて説明する。
図1は焼却炉に付設した焼却炉と焼却炉に付設した排煙処理装置の概略の構成を示す1部切欠き正面図であって、図中、符号1は装置を全体的に示す。
【0014】
この焼却炉2は、炉の内室を底部2aから立ち上げた区画壁3により上部で連通する燃焼部4と煙道部5とに区画され、燃焼部4の中間高さ位置にはロストル6が設けられており、ロストル6の下方には燃焼用バーナの火口部を臨ませた燃焼口7が設けてある。
【0015】
そして、ロストル6の上部の燃焼部側壁2bには焼却物投入口8が、ロストル6の下部の燃焼部側壁4aには灰掻き出し口9が夫々開口させてある。
また、煙道部5の上壁2c部分には排煙口10が形成されており、この排煙口10は後述する浮遊微粒子捕捉装置11に煙を供給する吸引管12が連結され、煙道部側壁2dには沈降物掻き出し口13が設けてある。
【0016】
これら焼却物投入口8、灰掻き出し口9、沈降物掻き出し口13は夫々蓋板 14で閉塞されるようになっている。
上記浮遊微粒子捕捉装置11は、水15を貯留した略直方体の密閉形の貯溜容器16と、貯溜容器16内の水15を吸水口17から吸引して加圧する加圧ポンプ18と、加圧ポンプ18で加圧された水15を噴射して負圧を形成する負圧形成手段19とを備えて構成されている。
【0017】
上記負圧形成手段19は、噴射ノズル20の前方に直管状の微粒子捕捉管21を形成してなり、噴射ノズル20と微粒子捕捉管21の噴射ノズル20側端部との間には吸引室22が形成されている。
この吸引室22には排煙吸引口23と外気吸引口24とが形成されており、排煙吸引口23は吸引管12で焼却炉2の排煙口10に連通させてあり、外気吸引口24には吸引される外気の量を制御する調節弁25が設けられている。
【0018】
また、貯溜容器16の上壁16aには貯溜容器16の内圧調節手段26と有蓋円筒状の遠心分離部27とが設けられており、遠心分離部27の側壁27aに微粒子捕捉管21の吐出口28が接線状に開口させてある。
【0019】
内圧調節手段26は、貯溜容器16の上壁16aに形成されたリリーフ孔29をスプリング30でボール状の弁体31で閉塞に付勢して構成されており、弁体31を開けてリリーフ孔29から放出される調圧用気体は放出口32から外部に放出される。
また、密閉形の貯溜容器16に貯溜された水15の液面上には空間部分(上部空間)33が形成されており、この空間部分33は焼却炉2の燃焼口7に送風路34で連結されている。
【0020】
この送風路34にはその燃焼口7寄り部分に燃料装置35からの燃料が注入されて混合されてから燃焼口7に供給されるようになっている。
上述のように焼却炉2と浮遊微粒子捕捉装置11とは吸引管12及び送風路34とで連結されて焼却炉2からの排煙がリサイクルされて直接外部には漏れないクローズドシステムの排煙処理方式になっている。
【0021】
上記のように構成された焼却炉における排煙処理装置1の作動を次に説明する。
先ず、加圧ポンプ18を駆動して貯溜容器16内の水を加圧して噴射ノズル20に供給し、噴射ノズル20から微粒子捕捉管21に直線状に噴射させる。
微粒子捕捉管21に噴射された高圧の流体は複数の粒状(霧滴)となって飛翔する時、飛翔するジェット流36の水の粒子とその周囲の静止しようとする気体との間にベルヌーイの定理の速度差による負圧を生じるとともに、微粒子捕捉管を飛翔するジェット流36の水の粒子の前面部分は空気を圧縮しながら流走する。
【0022】
そして、このジェット流36の水の粒子がその周囲に負圧を形成し、その粒子の前面部分では空気を圧縮しながら微粒子捕捉管21を飛翔して流走して徐々に広がってゆき、これが微粒子捕捉管21内一杯に広がった状態になる。
【0023】
ジェット流36の水の粒子が微粒子捕捉管21内一杯に広がった状態になると、粒子の周囲の負圧同士が融合し、この融合された負圧と、粒子の前面部分の圧縮された空気同士が合一されたものとの相乗作用により、恰も微粒子捕捉管の吐出口28側に向かって作用する連続状のピストンPのような作用をし、微粒子捕捉管21の噴射ノズル20の近傍には高圧で多量の負圧が形成される。
【0024】
こうして微粒子捕捉管21の噴射ノズル20の近傍に形成された負圧が吸引室内22に作用すると、吸引管12を介して焼却炉2の排煙を排煙口10から吸引室内22に吸引するとともに外気吸引口24からは調節弁25で調量された外気が吸引室内22に吸引される。
吸引室内22に吸引された排煙と外気とはジェット流とともに微粒子捕捉管21内を流走する時に負圧の強力なジェット流の周面部分からジェット流を形成する水の粒子に吸い寄せられる。従って、排煙及び外気すべてがジェット流の粒子に接触し、排煙中に含まれるダイオキシン等の有害物質や煤はジェット流を形成する水の粒子に付着して捕捉される。
【0025】
ダイオキシン等の有害物質や煤等を捕捉したジェット流は遠心分離部27に流入し、ここで旋回する時に固・気・液分離される。ここで固・気・液分離された固・液分は貯溜容器16内の水15に流下し、固体分は貯溜容器16の底部に沈降して堆積し、気体分は貯溜容器16の空間部分33に流入し、空間部分33の圧力を高める。
【0026】
貯溜容器16の空間部分33の圧力が高められると、この高められた圧力で空間部分33の空気が送風路34を通じて焼却炉2の燃焼口7に燃料とともに供給される。
【0027】
この時、燃焼口7に供給される空間部分33の空気は、燃焼排ガスとともに外気吸引口24から吸引された外気を含んでおり、この外気により焼却炉2の燃焼が促進されて焼却炉2内の温度を、合成樹脂を焼却する時にダイオキシン等の有害物質が発生し難い例えば800℃以上に保つことができる。
また、貯溜容器16の空間部分33の圧力が所定値より高くなると、内圧調節手段26の弁体31がスプリング30の弾性力に抗してリリーフ孔29を開き、貯溜容器16の空間部分33の空気を放出するので、貯溜容器16の空間部分323の圧力は常時所定値に保たれ、焼却炉2内の温度も上記の800℃以上の安定した状態に保たれる。
【0028】
ここで、焼却炉2の排煙口10から放出された時にミスト状で含まれる少量の有害物質が微粒子捕捉管21内のジェット流の水の粒子に余すところ無く捕捉されていることから、貯溜容器16の空間部分33の圧力が所定値に保つためにリリーフ孔29から放出される貯溜容器16の空間部分33の空気がそのまま大気中に放出されても、これが為に環境汚染等を引き起こすことは無い。
【0029】
尚、上記実施の形態では加圧ポンプ18で加圧された貯溜容器16内の水15を噴射ノズル20から微粒子捕捉管21に直接噴射するようにしてあるが、図2に示すように、噴射ノズル20と微粒子捕捉管21との間に保護管36を配設し、噴射ノズル20と保護管36との間に吸気口37を形成し、噴射ノズル20から噴射したジェット流で保護管36に負圧を形成するとともに、この負圧で吸気口37から吸引した空気を保護管36のジェット流に混合して混気ジェットを形成してからこの混気ジェットを保護管36から微粒子捕捉管21に噴射するようにすることもできる。
【0030】
こうした混気ジェットで微粒子捕捉管21に負圧を形成して排煙を吸引室内22に吸引する場合には、混気ジェット流に含まれる気泡が混気ジェット流と微粒子捕捉管21の内面との間の摩擦を軽減するので、微粒子捕捉管21内を流走する混気ジェット流の流勢の低下を防止して強力な負圧を形成できる。
【0031】
また、図3に示すように加圧ポンプ18で加圧された貯溜容器16内の水15を噴射する噴射ノズル20を大径の微粒子捕捉管21に対向させて複数設け、複数の噴射ノズル20からジェット流を微粒子捕捉管21に均等に噴射させるようにすると、ジェット流が微粒子捕捉管21内一杯に広がる位置が噴射ノズル10側に近づき、微粒子捕捉管21の管長を短縮できるので装置の小型化を図ることができる。
【0032】
更に、上記図3に示す複数の噴射ノズル20の前方に夫々保護管36を設けて混気ジェットを形成し、この混気ジェットを微粒子捕捉管21に噴射するようにすることもできる(図4参照)。
【0033】
この場合、微粒子捕捉管21は図5に示すように各保護管36に対応させた複数本で形成することもできるのは勿論のことである。
加えて、上記実施の形態では吸引室内22に外気吸引口24を形成するようにしてあるが、図2、図4、図5に示すように吸気口37で外気を吸引し、保護管36内で混気ジェットを形成する場合には吸引室内22に形成される外気吸引口24は吸気口37に兼用させることができるのは勿論のことである。
【0034】
【発明の効果】
本発明に係る焼却炉における排煙処理装置は以上に説明したように、吐出口が密閉可能な容器に開口する微粒子捕捉管に噴射されたジェット流で負圧を形成し、この負圧で焼却炉から排出される排煙を吸引し、微粒子捕捉管を流走するジェット流に吸引した排煙を接触させてその中に浮遊する微粒子を捕捉するとともに、微粒子を捕捉したジェット流は再び加圧ポンプで加圧しリサイクルできるようにしてあるので、従来のシャワーリング方式のように大量の水を必要とせずそのランニングコストを大幅に低減することができるという利点がある。
【0035】
しかも、ジェット流で発生させた負圧で浮遊微粒子を含んだ排煙を吸引するので、吸引された排煙中の微粒子は余すところなく水滴として流走するジェット流のに接触して捕捉されるので、従来のジェットスクラバー式のものに比べて微粒子の捕捉効率を格段に向上させることができる利点もある。
【0036】
また、ジェット流で発生させた負圧で排煙を吸引する一方、吐出口から吐出される排煙及び外気吸引口から吸引された外気により高くなった密閉可能な容器内の内圧を利用して焼却炉の燃焼口に送風するようにしてあるので、従来のようにように焼却炉の燃焼口に付設される送風装置を無くすことができる。
これにより、装置全体を小型にできるとともに、送風装置の駆動やその制御装置に要する費用や手間を無くせてイニシャルコストやランニングコストを更に低減させることができるという利点もある。
【0037】
更に、微粒子捕捉管の吐出口から密閉可能な容器の上部空間を介して燃焼口に至る送風路中に密閉可能な容器の内圧調節手段を設けたものでは、この内圧調節手段で密閉可能な容器の内圧を調節するだけで燃焼口への送風量を簡単に調節でき、燃焼温度も有害物質の発生し難い温度に設定でき、有害物質の発生を可及的防止して環境汚染を防止することができる利点もある。
【0038】
ジェットポンプを混気式ジェットポンプにしたものでは、保護管から微粒子捕捉管に噴射された混気ジェット流が微粒子捕捉管を流走する時、そのジェット流に含まれる気泡が混気ジェット流と微粒子捕捉管の内面との間の摩擦を軽減して混気ジェット流の流勢の低下を防止するので、混気ジェット流はその流勢を強い状態に維持でき強力な負圧を形成することができるという利点もある。
【図面の簡単な説明】
【図1】は焼却炉に付設した浮遊微粒子捕捉装置の概略の構成を示す1部切欠き側面図である。
【図2】はジェットポンプを混気式ジェットポンプにした場合の当該部分の縦断側面図である。
【図3】は複数の噴射ノズルでジェットポンプを形成した場合の当該部分の縦断側面図である。
【図4】は複数の噴射ノズルの前方に保護管を形成して混気ジェットポンプを形成した場合の当該部分の縦断側面図である。
【図5】は複数の噴射ノズルの前方に保護管を形成して混気ジェットポンプを形成するとともに、保護管の夫々に微粒子捕捉管を形成した場合の当該部分の縦断側面図である。
【符号の説明】
1・・・排煙処理装置
2・・・焼却炉
7・・・燃焼口
10・・・排煙口
11・・・浮遊微粒子捕捉装置
15・・・粒子捕捉用液体(水)
16・・・密閉可能な容器
18・・・加圧ポンプ
20・・・噴射ノズル
21・・・微粒子捕捉管
22・・・吸引室
24・・・外気吸引口
28・・・吐出口
33・・・上部空間
[0001]
[Industrial application fields]
The present invention relates to a flue gas treatment apparatus that captures mist-like suspended fine particles in flue gas discharged from, for example, an incinerator.
[0002]
[Prior art]
Smoke in the incinerator is a mixture of mist-like fine particles evaporated by heating and combustion and mixed in the exhaust. If the incinerated product contains synthetic resin, the synthetic resin is heated in this mist. Due to the decomposition, a large amount of fine particles of harmful substances such as dioxins are contained.
[0003]
When capturing fine particles of harmful substances such as dioxin contained in the flue gas from such an incinerator, for example, a filter (so-called bag filter) as shown in FIG. There is known a filter dust collector for filtering with a filter.
[0004]
However, in this bag filter type filter dust collector, although the dust collection rate is high, the pressure loss is as large as, for example, 100 to 200 mmAq, and the particle size that can be captured is generally 20 to 0.1 μm, particularly 0.1 μm or less. However, there is a problem in that an electrostatic dust collector having a large initial cost and a high running cost must be used in order to capture extremely fine mist particles.
[0005]
Therefore, a showering type cleaning tower (so-called jet scrubber) having a low initial cost and a low running cost as shown in FIG. 2 of JP-A-3-232514 is widely used.
[0006]
[Problems to be solved by the invention]
However, in the above-described shower ring type cleaning tower, water is supplied in the form of shower into the flue gas from the incinerator containing extremely minute mist-like particles, and the mist-like mist in the processing gas is supplied to the water droplets of the shower. There is a problem that a large amount of water is required because particles are brought into contact with each other.
[0007]
Further, in the case of capturing ultra fine mist particles in flue gas in contact with water supplied in a shower form, the so-called jet scrubber disclosed in JP-A-3-232514 is treated with water sprayed in a shower form. Since the gas is caused to flow, there is a problem that the contact efficiency with the processing gas is deteriorated.
Also, when shower water droplets are fed into stationary positive pressure or normal pressure flue gas, the water droplets push away the fine particles in the flue gas and fly away, so that the fine particles and the shower water droplets fly. In addition to low contact efficiency, the flow of shower-like water droplets tends to cause the smoke to flow along the direction of the shower.
[0008]
When a flow that flows in the downstream direction of the shower occurs in the processing gas in this way, the fine particles in the flue gas flow with the shower, and the contact between the microscopic mist particles in the flue gas and the water droplets in the shower is not performed well. There is also a problem that the trapping efficiency of the fine particles is greatly reduced.
Moreover, since generation | occurrence | production of harmful substances, such as dioxin contained in the flue gas from an incinerator, is easy to generate | occur | produce when combustion temperature is 800 degrees C or less, combustion temperature is set comparatively high.
[0009]
In order to increase the combustion temperature, a blower or the like is provided at the combustion port, and the air blown from the blower promotes combustion in the furnace and maintains the combustion temperature high. For this reason, the incinerator will be enlarged.
In addition, there is a problem that power consumption required for driving the motor of the blower is large, and not only the running cost is increased, but also control is required.
[0010]
The present invention has been proposed in view of the above-mentioned problems, and minimizes the generation of harmful substances contained in the flue gas discharged from the incinerator as much as possible, and forms a very fine mist such as generated harmful substances. To provide a flue gas treatment device in an incinerator that captures all the generation of particles and eliminates environmental pollution, and to make the incinerator and flue gas treatment device compact. It is intended.
[0011]
[Means for Solving the Problems]
In order to achieve the above object, a flue gas treatment apparatus in an incinerator according to the present invention comprises an incinerator and a floating particulate trapping device that captures suspended particulates in flue gas discharged from the incinerator. There are a combustion port for supplying fuel with the air blow or the air blow and a smoke exhaust port for discharging the combustion exhaust gas to the outside of the furnace, and the suspended particulate trapping device has a sealable container storing the liquid for capturing particles, and a discharge port. A particulate trap tube that opens in a sealable container, a pressurizing pump that pressurizes the liquid for trapping particles stored in the sealable container, and a pressure fluid pressurized by the pressurizing pump is injected into the particulate trapping pipe. A jet pump having a jet nozzle and a suction chamber formed between the fine particle capturing pipe and the jet nozzle, the suction chamber of the jet pump being in communication with the smoke outlet of the incinerator, the jet nozzle and the fine particles Outside air between the capture tube Provided with a 引口, it is characterized in that the upper space of the sealable container is connected to the combustion port.
[0012]
In addition, an internal pressure adjusting means for the sealable container is provided in the air passage extending from the discharge port of the particulate trapping tube to the combustion port through the upper space of the sealable container, and the jet pump is disposed in front of the injection nozzle. The pressurized fluid is injected into the protective tube from the injection nozzle to form a negative pressure in the protective tube, and air is sucked by the negative pressure formed in the protective tube to mix the fluid in the protective tube It is also one of the features that the mixed jet jet pump is configured to form a negative pressure in the particulate trapping pipe by jetting the mixed jet jet stream from the protective pipe to the particulate trapping pipe.
[0013]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments of a flue gas treatment apparatus in an incinerator according to the present invention will be described below with reference to the drawings.
FIG. 1 is a partially cutaway front view showing a schematic configuration of an incinerator attached to an incinerator and a flue gas treatment apparatus attached to the incinerator. In the figure, reference numeral 1 denotes the apparatus as a whole.
[0014]
The incinerator 2 is partitioned into a combustion section 4 and a flue section 5 communicating with each other at an upper portion by a partition wall 3 rising from the bottom 2 a of the inner chamber of the furnace. A combustion port 7 facing the crater portion of the combustion burner is provided below the rooster 6.
[0015]
An incinerated product inlet 8 is opened on the combustion section side wall 2b above the rooster 6 and an ash scraping opening 9 is opened on the combustion section side wall 4a below the rooster 6.
Further, a smoke exhaust port 10 is formed in the upper wall 2c portion of the flue portion 5, and this smoke exhaust port 10 is connected to a suction pipe 12 for supplying smoke to a floating particulate trap 11 which will be described later. A sediment scraping port 13 is provided in the partial side wall 2d.
[0016]
The incineration material inlet 8, the ash scraping port 9, and the sediment scraping port 13 are respectively closed by a cover plate 14.
The floating particulate trap 11 includes a substantially rectangular parallelepiped sealed storage container 16 storing water 15, a pressure pump 18 that sucks and pressurizes the water 15 in the storage container 16 from a water inlet 17, and a pressure pump And negative pressure forming means 19 for injecting water 15 pressurized at 18 to form a negative pressure.
[0017]
The negative pressure forming means 19 is formed with a straight tubular particle capturing tube 21 in front of the injection nozzle 20, and a suction chamber 22 is provided between the injection nozzle 20 and the end of the particle capturing tube 21 on the injection nozzle 20 side. Is formed.
A smoke exhaust suction port 23 and an outside air suction port 24 are formed in the suction chamber 22, and the smoke exhaust suction port 23 communicates with the smoke exhaust port 10 of the incinerator 2 through the suction pipe 12. 24 is provided with an adjustment valve 25 for controlling the amount of outside air to be sucked.
[0018]
Also, the upper wall 16a of the storage container 16 is provided with an internal pressure adjusting means 26 of the storage container 16 and a covered cylindrical centrifuge 27. The discharge port of the particulate trapping tube 21 is provided on the side wall 27a of the centrifuge 27. 28 is opened tangentially.
[0019]
The internal pressure adjusting means 26 is configured to urge a relief hole 29 formed in the upper wall 16a of the storage container 16 to be closed by a ball-shaped valve body 31 with a spring 30, and opens the valve body 31 to open a relief hole. The pressure adjusting gas discharged from 29 is discharged to the outside through the discharge port 32.
Further, a space portion (upper space) 33 is formed on the liquid level of the water 15 stored in the sealed storage container 16, and this space portion 33 is connected to the combustion port 7 of the incinerator 2 by the air passage 34. It is connected.
[0020]
The air from the fuel device 35 is injected into the air passage 34 near the combustion port 7 and mixed to be supplied to the combustion port 7.
As described above, the incinerator 2 and the suspended particulate trap 11 are connected by the suction pipe 12 and the air passage 34 so that the exhaust gas from the incinerator 2 is recycled and does not leak directly to the outside. It is a method.
[0021]
Next, the operation of the flue gas treatment apparatus 1 in the incinerator configured as described above will be described.
First, the pressurizing pump 18 is driven to pressurize the water in the storage container 16 and supply the water to the injection nozzle 20, and the linear injection is performed from the injection nozzle 20 to the fine particle capturing pipe 21.
When the high-pressure fluid jetted to the particulate trapping tube 21 flies in a plurality of granular forms (mist droplets), the Bernoulli's fluid flows between the flying water particles of the jet stream 36 and the surrounding stationary gas. While generating a negative pressure due to the velocity difference of the theorem, the front part of the water particles of the jet stream 36 flying in the particulate trapping tube flows while compressing the air.
[0022]
Then, the water particles in the jet flow 36 form a negative pressure around the particles, and in the front part of the particles, the air is compressed while air flies and travels through the fine particle capturing tube 21 and gradually spreads. The particle trap tube 21 is fully expanded.
[0023]
When the water particles of the jet stream 36 are fully expanded in the fine particle capturing tube 21, the negative pressures around the particles are fused together, and the fused negative pressure and the compressed air in the front part of the particles are fused together. As a result of the synergistic action with the combined particles, the soot acts like a continuous piston P acting toward the discharge port 28 side of the particulate trapping pipe, and in the vicinity of the injection nozzle 20 of the particulate trapping pipe 21. A large amount of negative pressure is formed at high pressure.
[0024]
When the negative pressure formed in the vicinity of the injection nozzle 20 of the fine particle capturing pipe 21 acts on the suction chamber 22 in this way, the smoke exhausted from the incinerator 2 is sucked into the suction chamber 22 through the suction pipe 12 from the smoke outlet 10. Outside air metered by the control valve 25 is sucked into the suction chamber 22 from the outside air suction port 24.
The smoke and the outside air sucked into the suction chamber 22 are attracted to the water particles forming the jet flow from the peripheral surface portion of the strong negative jet flow along with the jet flow. Therefore, all of the flue gas and the outside air come into contact with the particles of the jet stream, and harmful substances such as dioxins and soot contained in the flue gas adhere to the water particles forming the jet stream and are captured.
[0025]
A jet stream that captures harmful substances such as dioxins and soot flows into the centrifugal separation unit 27 and is separated into solid, gas, and liquid when swirling here. Here, the solid, liquid, and liquid separated are flown down into the water 15 in the storage container 16, the solid is settled and deposited on the bottom of the storage container 16, and the gas is a space portion of the storage container 16. The pressure in the space 33 is increased.
[0026]
When the pressure in the space portion 33 of the storage container 16 is increased, the air in the space portion 33 is supplied with the fuel to the combustion port 7 of the incinerator 2 through the air passage 34 with the increased pressure.
[0027]
At this time, the air in the space portion 33 supplied to the combustion port 7 includes the outside air sucked from the outside air suction port 24 together with the combustion exhaust gas. The combustion of the incinerator 2 is promoted by this outside air, and the inside of the incinerator 2 This temperature can be maintained at, for example, 800 ° C. or higher, at which a harmful substance such as dioxin is hardly generated when the synthetic resin is incinerated.
Further, when the pressure in the space portion 33 of the storage container 16 becomes higher than a predetermined value, the valve body 31 of the internal pressure adjusting means 26 opens the relief hole 29 against the elastic force of the spring 30, and the space portion 33 of the storage container 16. Since air is discharged, the pressure in the space portion 323 of the storage container 16 is always maintained at a predetermined value, and the temperature in the incinerator 2 is also maintained in a stable state of 800 ° C. or higher.
[0028]
Here, since a small amount of harmful substances contained in the form of mist when released from the smoke exhaust port 10 of the incinerator 2 are trapped in the water particles of the jet flow in the particulate trapping pipe 21, Even if the air in the space portion 33 of the storage container 16 discharged from the relief hole 29 in order to keep the pressure in the space portion 33 of the container 16 at a predetermined value, this causes environmental pollution and the like. There is no.
[0029]
In the above embodiment, the water 15 in the storage container 16 pressurized by the pressurizing pump 18 is directly injected from the injection nozzle 20 to the fine particle capturing pipe 21, but as shown in FIG. A protective tube 36 is disposed between the nozzle 20 and the particulate trapping tube 21, an intake port 37 is formed between the spray nozzle 20 and the protective tube 36, and the jet stream ejected from the spray nozzle 20 forms a protective tube 36. In addition to forming a negative pressure, the air sucked from the intake port 37 with this negative pressure is mixed with the jet flow of the protective tube 36 to form an air-mixed jet, and then the mixed air jet is passed from the protective tube 36 to the particulate trapping tube 21. It can also be made to inject into.
[0030]
When such a mixed jet forms a negative pressure in the particulate trap tube 21 to suck the exhaust gas into the suction chamber 22, bubbles contained in the mixed jet flow are mixed with the mixed jet flow and the inner surface of the particulate trap tube 21. Therefore, it is possible to prevent a decrease in the flow force of the mixed jet flowing in the fine particle capturing pipe 21 and to form a strong negative pressure.
[0031]
Further, as shown in FIG. 3, a plurality of injection nozzles 20 for injecting water 15 in the storage container 16 pressurized by the pressure pump 18 are provided so as to face the large-diameter particle capturing pipe 21, and the plurality of injection nozzles 20 are provided. If the jet stream is sprayed evenly onto the particulate trap tube 21, the position where the jet stream spreads in the particulate trap tube 21 approaches the jet nozzle 10 side, and the length of the particulate trap tube 21 can be shortened. Can be achieved.
[0032]
Further, a protective tube 36 may be provided in front of each of the plurality of injection nozzles 20 shown in FIG. 3 to form an air mixture jet, and this air mixture jet may be injected into the particulate trapping tube 21 (FIG. 4). reference).
[0033]
In this case, as a matter of course, the fine particle capturing tube 21 can be formed by a plurality of tubes corresponding to the protective tubes 36 as shown in FIG.
In addition, in the above embodiment, the outside air suction port 24 is formed in the suction chamber 22, but as shown in FIGS. 2, 4, and 5, the outside air is sucked through the suction port 37, and the inside of the protective tube 36. Of course, when the air-fuel mixture jet is formed, the outside air suction port 24 formed in the suction chamber 22 can also be used as the air intake port 37.
[0034]
【The invention's effect】
As described above, the flue gas treatment apparatus in the incinerator according to the present invention forms a negative pressure by the jet flow injected into the fine particle capturing pipe opened in the container whose discharge port can be sealed, and incinerate at this negative pressure. The smoke exhausted from the furnace is sucked, and the sucked smoke is brought into contact with the jet stream flowing through the particulate trapping tube to trap the suspended particulates, and the jet stream capturing the particulates is pressurized again. Since it can be pressurized and recycled with a pump, there is an advantage that the running cost can be greatly reduced without requiring a large amount of water as in the conventional showering system.
[0035]
In addition, since the exhaust smoke containing suspended particulates is sucked in by the negative pressure generated by the jet flow, the fine particles in the sucked exhaust smoke are captured in contact with the jet stream that runs as water droplets. Therefore, there is an advantage that the trapping efficiency of the fine particles can be remarkably improved as compared with the conventional jet scrubber type.
[0036]
In addition, while exhausting the smoke with the negative pressure generated by the jet flow, using the internal pressure in the sealable container that is increased by the exhaust gas discharged from the discharge port and the outside air sucked from the outside air suction port Since the air is blown to the combustion port of the incinerator, the blower attached to the combustion port of the incinerator can be eliminated as in the prior art.
As a result, the entire apparatus can be reduced in size, and there is an advantage that the initial cost and the running cost can be further reduced by eliminating the cost and labor required for driving the blower and its controller.
[0037]
Further, in the case where the internal pressure adjusting means of the sealable container is provided in the air passage extending from the discharge port of the fine particle capturing pipe to the combustion port through the upper space of the sealable container, the container that can be sealed by the internal pressure adjusting means By simply adjusting the internal pressure, the amount of air blown to the combustion port can be easily adjusted, the combustion temperature can be set to a temperature at which no harmful substances are generated, and the generation of harmful substances is prevented as much as possible to prevent environmental pollution. There is also an advantage that can be.
[0038]
In the case where the jet pump is a mixed-type jet pump, when the mixed-jet flow injected from the protective tube to the particulate trapping tube flows through the particulate trapping tube, the bubbles contained in the jet flow are mixed with the mixed-jet flow. Friction with the inner surface of the particulate trap tube is reduced to prevent a decrease in the flow rate of the mixed jet flow, so that the mixed jet flow can maintain the flow in a strong state and form a strong negative pressure There is also an advantage of being able to.
[Brief description of the drawings]
FIG. 1 is a partially cutaway side view showing a schematic configuration of a suspended particulate trap attached to an incinerator.
FIG. 2 is a longitudinal side view of the portion when the jet pump is an air-mixing type jet pump.
FIG. 3 is a longitudinal side view of the portion in the case where a jet pump is formed by a plurality of injection nozzles.
FIG. 4 is a vertical side view of the portion in the case where a mixed tube is formed by forming a protective tube in front of a plurality of injection nozzles.
FIG. 5 is a longitudinal side view of a portion where a protective tube is formed in front of a plurality of injection nozzles to form an air-mixing jet pump and a particulate trapping tube is formed in each of the protective tubes.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 ... Smoke treatment apparatus 2 ... Incinerator 7 ... Combustion port 10 ... Smoke exit 11 ... Floating particulate capture device 15 ... Liquid for particle capture (water)
16 ... Sealable container 18 ... Pressure pump 20 ... Injection nozzle 21 ... Particulate trap tube 22 ... Suction chamber 24 ... Outside air suction port 28 ... Discharge port 33 ...・ Upper space

Claims (3)

焼却炉と焼却炉から排出される排煙中の浮遊微粒子を捕捉する浮遊微粒子捕捉装置とからなり、焼却炉は、送風または送風とともに燃料を供給する燃焼口と、燃焼排ガスを炉外に放出する排煙口とを有し、浮遊微粒子捕捉装置は、粒子捕捉用液体を貯溜した密閉可能な容器と、吐出口が密閉可能な容器に開口する微粒子捕捉管と、密閉可能な容器に貯溜された粒子捕捉用液体を加圧する加圧ポンプと、該加圧ポンプで加圧された圧力流体を微粒子捕捉管に噴射する噴射ノズルと、微粒子捕捉管と噴射ノズルとの間に形成された吸引室とを備えたジェットポンプを有し、該ジェットポンプの吸引室を焼却炉の排煙口と連通させ、噴射ノズルと微粒子捕捉管との間に外気吸引口を設けるとともに、密閉可能な容器の上部空間を燃焼口に連結させたことを特徴とする焼却炉における排煙処理装置。Composed of an incinerator and a suspended particulate trap that captures suspended particulates discharged from the incinerator, and the incinerator discharges combustion exhaust gas to the outside of the furnace, supplying a combustion port that supplies fuel along with blowing or blowing. The suspended particulate trapping device having a smoke exhaust port is stored in a sealable container that stores a liquid for capturing particles, a particulate trap tube in which a discharge port opens to the sealable container, and a sealable container. A pressurizing pump for pressurizing the particle capturing liquid, an injection nozzle for injecting a pressure fluid pressurized by the pressurizing pump to the microparticle capturing tube, and a suction chamber formed between the microparticle capturing tube and the spraying nozzle; The jet pump has a jet pump, the suction chamber of the jet pump communicates with the smoke exhaust port of the incinerator, an outside air suction port is provided between the injection nozzle and the particulate trap tube, and the upper space of the sealable container Connected to the combustion port Flue gas treatment apparatus in the incinerator characterized and. 微粒子捕捉管の吐出口から密閉可能な容器の上部空間を介して燃焼口に至る送風路中に密閉可能な容器の内圧調節手段を設けたことを特徴とする請求項1に記載の焼却炉における排煙処理装置。2. The incinerator according to claim 1, wherein an internal pressure adjusting means for the sealable container is provided in an air passage extending from the discharge port of the fine particle capturing pipe to the combustion port through the upper space of the sealable container. Smoke removal equipment. ジェットポンプが、噴射ノズルの前方に保護管を設け、加圧された流体を噴射ノズルから保護管内に噴射して保護管内に負圧を形成し、当該保護管内に形成された負圧で空気を吸引して保護管内の流体を混気ジェット流にし、該混気ジェットジェット流を保護管から微粒子捕捉管に噴射して微粒子捕捉管内に負圧を形成する混気式ジェットポンプにしたことを特徴とする請求項1または請求項2に記載の焼却炉における排煙処理装置。The jet pump has a protective tube in front of the injection nozzle, injects pressurized fluid into the protective tube from the injection nozzle to form a negative pressure in the protective tube, and air is generated by the negative pressure formed in the protective tube. A mixed-air jet pump that sucks the fluid in the protective tube into a mixed-jet flow and injects the mixed-jet flow from the protective tube to the particulate trap tube to form a negative pressure in the particulate trap tube. A flue gas treatment apparatus in an incinerator according to claim 1 or 2.
JP14126398A 1998-05-22 1998-05-22 Flue gas treatment equipment in an incinerator Expired - Fee Related JP4017252B2 (en)

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CN108273361B (en) * 2018-02-01 2024-02-20 中冶焦耐(大连)工程技术有限公司 A safe incineration process for asphalt smoke tail gas
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