JPH0140680B2 - - Google Patents
Info
- Publication number
- JPH0140680B2 JPH0140680B2 JP56006204A JP620481A JPH0140680B2 JP H0140680 B2 JPH0140680 B2 JP H0140680B2 JP 56006204 A JP56006204 A JP 56006204A JP 620481 A JP620481 A JP 620481A JP H0140680 B2 JPH0140680 B2 JP H0140680B2
- Authority
- JP
- Japan
- Prior art keywords
- smoke
- separated
- smoke washing
- wastewater
- mother liquor
- 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
- 239000000779 smoke Substances 0.000 claims description 56
- 239000002351 wastewater Substances 0.000 claims description 55
- 238000005406 washing Methods 0.000 claims description 45
- 229910001385 heavy metal Inorganic materials 0.000 claims description 28
- 238000000034 method Methods 0.000 claims description 27
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims description 22
- 150000003839 salts Chemical class 0.000 claims description 21
- 239000012452 mother liquor Substances 0.000 claims description 20
- 238000004062 sedimentation Methods 0.000 claims description 12
- 239000013522 chelant Substances 0.000 claims description 11
- 239000011347 resin Substances 0.000 claims description 11
- 229920005989 resin Polymers 0.000 claims description 11
- 239000011780 sodium chloride Substances 0.000 claims description 11
- 238000005345 coagulation Methods 0.000 claims description 10
- 230000015271 coagulation Effects 0.000 claims description 10
- 238000000926 separation method Methods 0.000 claims description 8
- 238000001179 sorption measurement Methods 0.000 claims description 5
- 238000010438 heat treatment Methods 0.000 claims description 4
- 238000009833 condensation Methods 0.000 claims 1
- 230000005494 condensation Effects 0.000 claims 1
- 238000003795 desorption Methods 0.000 claims 1
- 238000004140 cleaning Methods 0.000 description 11
- 238000001816 cooling Methods 0.000 description 9
- 239000000126 substance Substances 0.000 description 9
- 238000002156 mixing Methods 0.000 description 5
- 239000007788 liquid Substances 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 3
- 239000010446 mirabilite Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 230000008023 solidification Effects 0.000 description 3
- 238000007711 solidification Methods 0.000 description 3
- 239000003513 alkali Substances 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000010612 desalination reaction Methods 0.000 description 2
- 238000011033 desalting Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 230000000704 physical effect Effects 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 239000002516 radical scavenger Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- RSIJVJUOQBWMIM-UHFFFAOYSA-L sodium sulfate decahydrate Chemical compound O.O.O.O.O.O.O.O.O.O.[Na+].[Na+].[O-]S([O-])(=O)=O RSIJVJUOQBWMIM-UHFFFAOYSA-L 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000011505 plaster Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 238000004056 waste incineration Methods 0.000 description 1
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
- Removal Of Specific Substances (AREA)
Description
本発明は焼却炉の排ガスを洗浄処理して発生す
る洗煙排水の処理方法に関するものである。
焼却炉の排ガス中には燃焼生成物としてCO2、
H2OやSOx、NOx、HCl、過剰空気等のガス成
分の他、灰分、未燃分等被焼却物の性状あるいは
燃焼条件により各種成分が混入している。
このうち、有害成分であるSOx、NOx、HCl
等を除去するための各種の対索が提案され、
SOx、HCl等に対しては湿式又は乾式のスクラバ
が多用されている。特に、その除去率を向上する
ためにはアルカリを洗浄液とした湿式スクラバの
使用が一般的であり、この場合、上記酸性ガスと
アルカリとの反応の結果洗浄液中には、塩類が生
成し、又ダスト成分も補促される。洗浄生成物
は、ある濃度に達すると洗煙排水として系外に引
き抜かれ処分される必要がある。
上記洗煙排水中の生成物は主成分の塩類の他各
種有害重金属も含有するため直接廃棄はできず、
従来は、固化剤による固化処理または重金属分離
後固化処理等による処分が行なわれていたが、完
全な溶出防止は行ない難く洗煙排水の処分に困難
を来たしていた。
また、洗煙排水の処理方法として、加熱濃縮し
て塩を晶出させる場合、重金属類及びNa2SO4等
の除去工程を採用することはこれまでの情報でも
知られている。すなわち、Na2SO4除去方法とし
てはCaCl2を添加してNa2SO4+CaCl2→CaSO4+
2NaClの様に石膏の形に変換後取り出している。
この方法では過剰のCaCl2あるいは溶解度の範囲
で残存するCaSO4が系内の蒸発缶等に析出して所
謂スケールとして付着するため処理装置を運転す
る上で障害となり、したがつて、定期的な洗浄作
業を行なうか、Ca塩類除去工程を別途付加する
ことの必要があつた。
本発明は、焼却炉の洗煙排水を、凝集沈殿およ
びキレート樹脂吸着処理により上記洗煙排水中の
重金属類を除去する重金属除去工程と、加燃濃縮
して上記洗煙排水中のNaClを晶出分離する脱食
塩工程と、分離して得られる分離母液を冷却して
上記分離母液中のNa2SO4を晶出分離する脱芒工
程との組合せによつて処理することを特徴とし、
その目的とするところは、上記従来の欠点を解消
し、洗煙排水の処分と共に含有塩類を精製塩とし
て回収し、有効利用するための回収方法も兼ねた
焼却炉洗煙排水の処理方法を提供するものであ
る。
このように構成されている本発明において、洗
煙排水を凝集沈殿処理して重金属を除去し、さら
に重金属捕集剤、キレート樹脂処理等でHgを高
いレベルで除去してから加燃濃縮することにより
NaClを晶出分離する。この分離母液を35℃以下
に冷却してNa2SO4を晶出分離することにより精
選塩(NaCl)及び芒硝(Na2SO4)を回収する。
このように本発明は、焼却炉の洗煙排水を、凝
集沈殿およびキレート樹脂吸着処理により上記洗
煙排水中の重金属類を除去する重金属除去工程
と、加燃濃縮して上記洗煙排水中のNaClを晶出
分離する脱食塩工程と、分離して得られる分離母
液を冷却して上記分離母液中のNa2SO4を晶出分
離する脱芒工程との組合せによつて処理するの
で、洗煙排水中の塩類の他各種有害重金属が十分
に除去され、したがつて、本発明に係る方法によ
る処理済の洗煙排水の処分がきわめて容易なもの
となる。
また、洗煙排水中の含有塩類を、加燃濃縮して
NaClを晶出分離させて精製塩として回収するの
で、洗煙排水中の収資源化としてきわめて有効な
方法である。
さらに、洗煙排水中の含有塩類を回収するにあ
たつて、上記洗煙排水を加燃濃縮して上記洗煙排
水中のNaClを晶出分離させたのち、分離して得
られた分離母液を冷却し、Na2SO4の溶解度が35
℃以下に於て急激に減少する物性を利用して
Na2SO4除去を行なうため従来のように残存
CaCl2の析出によるトラブルがなく、また薬品添
加工程も減り、かつ、本発明を適用する装置の運
転管理を容易にすると共に副生芒硝を利用し得る
ことが出来る。
以下、本発明の好ましい一実施例を第1図に示
す実施例に基づいて説明する第1図において、洗
煙排水11の供給ライン12の後流側に薬液混和
槽1、凝集沈殿槽2、過塔3、キレート樹脂塔
4、蒸発濃縮缶5、遠心分離機6が配設されてお
り、また、遠心分離機6からの分離母液13の返
送ライン14には冷却塔7、遠心分離機8が介設
され同返送ライン14の後流側14aは薬液混和
槽1の上流側の洗煙排水供給ライン12に返送さ
れている。
なおは晶出分離したNaCl、は晶出分離し
たNa2SO4、11aは重金属類が除去された洗煙
排水、13aはNa2SO4が分離除去された残存
母液、15,16はラインである。
本実施例は、第1図に図示するフローにおい
て、煙却炉の洗煙排水11を、凝集沈殿槽2の凝
集沈殿およびキレート樹脂塔4でのキレート樹脂
吸着処理により洗煙排水11中の重金属類を除去
する重金属除去工程と、蒸発濃縮缶5で加燃濃
縮して洗煙排水11a中のNaCl9を晶出分離す
る脱食塩工程と、遠心分離機6で分離して得ら
れる分離母液13を冷却塔7で冷却して分離母液
13のNa2SO4を晶出分離する脱芒工程との
組合せによつて処理するものである。
さらに、本実施例を詳述すれば洗煙排水11を
洗煙排水供給ライン12から薬液混和槽1に供給
し、同槽1においてFeCl3、Na2Sまたは重金属捕
集剤、高分子凝集剤、PH調整剤等と混合し、つい
で凝集沈殿槽2にて洗煙排水11中の重金属類を
沈降除去する。
なお、処理する洗煙排水の性状の一例を第1表
に示す。
The present invention relates to a method for treating smoke cleaning wastewater generated by cleaning exhaust gas from an incinerator. The exhaust gas of the incinerator contains CO 2 as combustion products,
In addition to gas components such as H 2 O, SOx, NOx, HCl, and excess air, various components such as ash and unburned matter are mixed in depending on the properties of the material to be incinerated or combustion conditions. Of these, the harmful components SOx, NOx, and HCl
Various pairing methods have been proposed to remove
Wet or dry scrubbers are often used for SOx, HCl, etc. In particular, in order to improve the removal rate, it is common to use a wet scrubber that uses alkali as the cleaning liquid.In this case, salts are generated in the cleaning liquid as a result of the reaction between the acidic gas and the alkali, and Dust components are also supplemented. When the cleaning product reaches a certain concentration, it must be drawn out of the system as smoke cleaning wastewater and disposed of. The products in the smoke washing wastewater cannot be directly disposed of because they contain salts, which are the main components, and various toxic heavy metals.
Conventionally, disposal has been carried out by solidification treatment using a solidification agent or solidification treatment after heavy metal separation, but it has been difficult to completely prevent elution, making it difficult to dispose of smoke washing wastewater. In addition, as a method for treating smoke washing wastewater, it is known from previous information that when heating and concentrating to crystallize salts, a process for removing heavy metals, Na 2 SO 4 , etc. is adopted. In other words, as a method for removing Na 2 SO 4 , CaCl 2 is added and Na 2 SO 4 + CaCl 2 → CaSO 4 +
Like 2NaCl, it is converted into plaster form and then extracted.
In this method, excess CaCl 2 or CaSO 4 remaining within the solubility range precipitates on the evaporator etc. in the system and adheres as so-called scale, which becomes an obstacle to the operation of the processing equipment. It was necessary to perform cleaning work or add a separate step to remove Ca salts. The present invention includes a heavy metal removal process in which heavy metals are removed from the smoke washing wastewater from an incinerator through coagulation sedimentation and chelate resin adsorption treatment, and a heavy metal removal process in which heavy metals are removed from the smoke washing wastewater by heating and concentration to crystallize NaCl in the smoke washing wastewater. The treatment is characterized by a combination of a desalting step in which the salt is removed and separated, and a deawning step in which the separated mother liquor obtained by separation is cooled and Na 2 SO 4 in the separated mother liquor is crystallized and separated,
The purpose is to provide a method for treating incinerator smoke wastewater that eliminates the above-mentioned conventional drawbacks, and that also serves as a recovery method for disposing of the smoke wash wastewater and recovering the contained salts as purified salt for effective use. It is something to do. In the present invention configured as described above, heavy metals are removed by coagulation and sedimentation treatment of smoke washing wastewater, and Hg is further removed at a high level by treatment with a heavy metal scavenger, chelate resin, etc., and then combustion and concentration are performed. by
NaCl is crystallized and separated. The separated mother liquor is cooled to 35° C. or below to crystallize and separate Na 2 SO 4 to recover selected salt (NaCl) and Glauber's salt (Na 2 SO 4 ). As described above, the present invention includes a heavy metal removal step in which heavy metals are removed from the smoke washing wastewater from an incinerator through coagulation sedimentation and chelate resin adsorption treatment, and a heavy metal removal process in which heavy metals are removed from the smoke washing wastewater by burning and concentrating the smoke washing wastewater. The treatment is a combination of a desalting step in which NaCl is crystallized and separated, and a deawning step in which the separated mother liquor obtained by separation is cooled and Na 2 SO 4 in the separated mother liquor is crystallized and separated. Salts and various harmful heavy metals in the smoke wastewater are sufficiently removed, and therefore, the smoke washing wastewater treated by the method according to the present invention can be disposed of extremely easily. In addition, the salts contained in the smoke washing waste water are heated and concentrated.
Since NaCl is crystallized and separated and recovered as purified salt, this is an extremely effective method for recovering resources from smoke washing wastewater. Furthermore, in order to recover the salts contained in the smoke washing wastewater, the smoke washing wastewater is heated and concentrated to crystallize and separate NaCl in the smoke washing wastewater, and then the separated mother liquor obtained by separation is obtained. and the solubility of Na 2 SO 4 is 35
Utilizing the physical property that decreases rapidly below ℃
To remove Na 2 SO 4 , it remains as before.
There is no trouble caused by the precipitation of CaCl 2 , the number of chemical addition steps is reduced, and the operational management of the device to which the present invention is applied is facilitated, and by-product Glauber's salt can be used. Hereinafter, a preferred embodiment of the present invention will be explained based on the embodiment shown in FIG. 1. In FIG. 1, a chemical liquid mixing tank 1, a coagulation sedimentation tank 2, A filter tower 3, a chelate resin tower 4, an evaporative concentration can 5, and a centrifugal separator 6 are installed, and a cooling tower 7 and a centrifugal separator 8 are provided in the return line 14 for the separated mother liquor 13 from the centrifuge 6. is interposed, and the downstream side 14a of the return line 14 is returned to the smoke washing wastewater supply line 12 on the upstream side of the chemical mixing tank 1. 11a is the smoke washing wastewater from which heavy metals have been removed, 13a is the remaining mother liquor from which Na 2 SO 4 has been separated, and 15 and 16 are the lines. be. In this embodiment, in the flow shown in FIG. 1, the smoke washing waste water 11 of the smoke furnace is subjected to coagulation sedimentation in the coagulation-sedimentation tank 2 and chelate resin adsorption treatment in the chelate resin tower 4 to collect the heavy metals in the smoke washing waste water 11. a heavy metal removal process to remove metals, a desalination process to crystallize and separate NaCl9 in the smoke washing wastewater 11a by burning and concentrating in an evaporative concentrator 5, and a separation mother liquor 13 obtained by separating in a centrifuge 6. This treatment is carried out in combination with a de-awning process in which Na 2 SO 4 in the separated mother liquor 13 is crystallized and separated by cooling in a cooling tower 7 . Further, to describe this embodiment in detail, the smoke washing waste water 11 is supplied from the smoke washing waste water supply line 12 to the chemical solution mixing tank 1, and in the same tank 1, FeCl 3 , Na 2 S, a heavy metal scavenger, a polymer flocculant, etc. , PH adjuster, etc., and then in a coagulation sedimentation tank 2, heavy metals in the smoke washing waste water 11 are sedimented and removed. Table 1 shows an example of the properties of the smoke washing wastewater to be treated.
【表】【table】
【表】
ついで、凝集沈殿槽2から洗煙排水11を過
塔3に導き、同過塔3にて洗煙排水11中の微
細の懸濁物を分離し、さらにキレート樹脂塔4に
導き、同塔4にて洗煙排水11中に極微量に残存
するHgを吸着除去する。以上の重金属除去工程
に終えた洗煙排水11aを蒸発濃縮缶5に導
き、同缶5で加熱濃縮して洗煙排水11a中の
NaCl9を晶出させたのち、遠心分離機6で分離
母液13とNaCl9とに分離し精製塩としてライ
ン15から取り出す。なお、ライン15から取り
出された精製塩の性状の一例を第2表に示す。[Table] Next, the smoke washing waste water 11 is led from the coagulation sedimentation tank 2 to the filter tower 3, where the fine suspended matter in the smoke washing waste water 11 is separated, and further led to the chelate resin tower 4. The very small amount of Hg remaining in the smoke washing waste water 11 is adsorbed and removed in the same column 4. The smoke washing wastewater 11a that has been subjected to the above heavy metal removal process is led to the evaporative concentration can 5, where it is heated and concentrated to remove the smoke washing wastewater 11a.
After NaCl 9 is crystallized, it is separated into separated mother liquor 13 and NaCl 9 using a centrifuge 6 and taken out through line 15 as purified salt. An example of the properties of the purified salt taken out from line 15 is shown in Table 2.
【表】
一方、分離母液13には返送ライン14を通り
冷却槽7に導かれ、同槽7にて35℃以下に冷却
され、分離母液13中のNa2SO410を晶出させ
たのち遠心分離機8にかけNa2SO410をライン
16から取り出す。一方の残存母液13aは薬液
混和槽1の入口の洗煙排水供給ライン12に返送
し、新しい洗煙排水11と混合して上記のような
循環処理を行なう。
このように本実施例は、焼却炉の洗煙排水11
を、薬注タンク1で薬注後、凝集沈殿槽2で凝集
沈殿および過塔3で過後キレート樹脂4でキ
レート樹脂吸着処理することにより洗煙排水11
中の重金属類を除去する重金属除去工程と、重
金属が除去された洗煙排水11aを蒸発濃縮缶5
で加熱濃縮して洗煙排水11a中のNaCl9を晶
出させたのち遠心分離機6は分離してライン15
から回収する脱食塩工程と、遠心分離機6で分
離して得られる分離母液13を返送ライン14か
ら冷却塔7に導き、同冷却塔7で冷却して分離母
液13のNa2SO410を晶出させたのち遠心分離
機8で分離させライン16からNa2SO410を回
収する脱芒工程との組合せによつて処理するの
で、洗煙排水11中の塩類の他各種有害重金属が
十分に除去され、本実施例に係る方法による処理
済の洗煙排水の処分がきわめて容易なものとな
る。
また、洗煙排水11中の含有塩類を、有害な重
金属を除去したのち蒸発濃縮缶5で加熱濃縮して
NaCl9を晶出させ遠心分離機6で分離させて精
製塩として回収するので、洗煙排水11中の収資
源化としてきわめて有効な方法である。
さらに、洗煙排水11中の含有塩類を回収する
にあたつて、洗煙排水11aを蒸発濃縮缶5で加
熱濃縮して洗煙排水11a中のNaCl9を晶出さ
せ遠心分離機6で分離させたのち、遠心分離機6
で分離して得られた分離母液13を返送ライン1
4から冷却塔7に導き、同冷炉塔7で冷却し、
Na2SO4の溶解度が35℃以下に於て急激に減少す
る物性を利用してNa2SO4除去を行なうため従来
のように残存CaSO4の析出によるトラブルがな
く、また薬品添加工程も減り、かつ本実施例を適
当する運転管理装置の運転管理を容易にすると共
に副生芒硝を利用し得ることが出来る。
本発明は、上記の実施例においても詳述したよ
うに、洗煙排水の処分と共に含有塩類を精製塩と
して回収して有効利用するための回収方法である
ので、ごみ焼却炉排ガス洗浄装置、産業廃棄物焼
却排ガス洗浄装置、その他HCl、SOx含有排ガス
洗浄装置などから排出される洗煙排水の処理に適
したものである。[Table] On the other hand, the separated mother liquor 13 is led through the return line 14 to the cooling tank 7, where it is cooled to 35°C or lower to crystallize Na 2 SO 4 10 in the separated mother liquor 13. Centrifuge 8 takes Na 2 SO 4 10 out through line 16. One of the remaining mother liquors 13a is returned to the smoke washing waste water supply line 12 at the entrance of the chemical liquid mixing tank 1, mixed with new smoke washing waste water 11, and subjected to the above-mentioned circulation treatment. In this way, in this embodiment, the incinerator smoke waste water 11
After chemical injection in the chemical injection tank 1, coagulation and sedimentation in the coagulation-sedimentation tank 2, filtering in the filter tower 3, and chelate resin adsorption treatment with the chelate resin 4, resulting in smoke washing wastewater 11.
A heavy metal removal process for removing heavy metals in the smoke cleaning waste water 11a from which heavy metals have been removed is carried out in an evaporation concentrator 5.
After heating and concentrating the NaCl9 in the smoke washing wastewater 11a, the centrifuge 6 separates it and sends it to the line 15.
The separated mother liquor 13 obtained by separation with the centrifuge 6 is led to the cooling tower 7 through the return line 14, and is cooled in the cooling tower 7 to remove Na 2 SO 4 10 of the separated mother liquor 13. Since the treatment is combined with a de-awning process in which Na 2 SO 4 10 is recovered from the line 16 by separating it in a centrifuge 8 after crystallization, the salts and various harmful heavy metals in the smoke washing waste water 11 are sufficiently removed. This makes it extremely easy to dispose of the smoke washing wastewater that has been treated by the method according to this embodiment. In addition, the salts contained in the smoke washing waste water 11 are heated and concentrated in the evaporative concentrator 5 after removing harmful heavy metals.
Since NaCl 9 is crystallized and separated by the centrifuge 6 and recovered as purified salt, this is an extremely effective method for recovering resources from the smoke washing wastewater 11. Further, in recovering the salts contained in the smoke washing wastewater 11, the smoke washing wastewater 11a is heated and concentrated in the evaporative concentrator 5 to crystallize NaCl9 in the smoke washing wastewater 11a, and then separated in the centrifuge 6. Later, centrifuge 6
The separated mother liquor 13 obtained by separation is sent to the return line 1.
4 to the cooling tower 7, cooled in the same cooling furnace tower 7,
Since Na 2 SO 4 is removed by utilizing the physical property that the solubility of Na 2 SO 4 rapidly decreases below 35°C, there is no trouble caused by the precipitation of residual CaSO 4 as in the conventional method, and the number of chemical addition steps is also reduced. In addition, it is possible to easily manage the operation of the operation control device to which this embodiment is applied, and to utilize the by-product mirabilite. As described in detail in the above embodiments, the present invention is a recovery method for disposing of smoke washing wastewater and recovering the contained salts as purified salt for effective use. It is suitable for treating smoke cleaning wastewater discharged from waste incineration exhaust gas cleaning equipment and other HCl and SOx-containing exhaust gas cleaning equipment.
第1図は本発明に係る一実施例のフローシイー
トである。
1……薬液混和槽、2……凝集沈殿槽、3……
過塔、4……キレート樹脂塔、5……蒸発濃縮
缶、6……遠心分離機、7……冷却塔、8……遠
心分離機、9……NaCl、10……Na2SO4、1
1,11a……洗煙排水、12……洗煙排水供給
ライン、13……分離母液、13a……残存母
液、14,14a……返送ライン、15,16…
…ライン、……重金属除去工程、……脱食塩
工程、……脱芒工程。
FIG. 1 is a flow sheet of an embodiment according to the present invention. 1... Chemical solution mixing tank, 2... Coagulation sedimentation tank, 3...
Passing tower, 4... Chelate resin tower, 5... Evaporation concentration can, 6... Centrifugal separator, 7... Cooling tower, 8... Centrifugal separator, 9... NaCl, 10... Na 2 SO 4 , 1
1, 11a... Smoke washing waste water, 12... Smoke washing waste water supply line, 13... Separated mother liquor, 13a... Residual mother liquor, 14, 14a... Return line, 15, 16...
...line, ...heavy metal removal process, ...desalination process, ...deawning process.
Claims (1)
ト樹脂吸着処理により上記洗煙排水中の重金属類
を除去する重金属除去工程と、加熱濃縮して上記
洗煙排水中のNaClを晶出分離する脱食塩工程と、
分離して得られる分離母液を冷却して上記分離母
液中のNa2SO4を晶出分離する脱芒工程との組合
せによつて処理することを特徴とする焼却炉洗煙
排水の処理方法。1 A heavy metal removal process in which heavy metals are removed from the incinerator smoke wastewater through coagulation sedimentation and chelate resin adsorption treatment, and a desorption process in which NaCl in the smoke wash wastewater is crystallized and separated by heating and condensation. salt process,
A method for treating incinerator smoke washing wastewater, characterized in that the treatment is carried out in combination with a de-awning step in which the separated mother liquor obtained by separation is cooled and Na 2 SO 4 in the separated mother liquor is crystallized and separated.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56006204A JPS57119897A (en) | 1981-01-19 | 1981-01-19 | Treatment of waste water of smoke scrubbing in incineration furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56006204A JPS57119897A (en) | 1981-01-19 | 1981-01-19 | Treatment of waste water of smoke scrubbing in incineration furnace |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57119897A JPS57119897A (en) | 1982-07-26 |
| JPH0140680B2 true JPH0140680B2 (en) | 1989-08-30 |
Family
ID=11632000
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56006204A Granted JPS57119897A (en) | 1981-01-19 | 1981-01-19 | Treatment of waste water of smoke scrubbing in incineration furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS57119897A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106145223A (en) * | 2016-08-01 | 2016-11-23 | 江苏星瑞化工工程科技有限公司 | A kind of processing method of high-salt wastewater |
-
1981
- 1981-01-19 JP JP56006204A patent/JPS57119897A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57119897A (en) | 1982-07-26 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP6101783B2 (en) | CO2 recovery system and CO2 recovery method | |
| JP3304300B2 (en) | Cement raw material processing method | |
| US4617180A (en) | Process for purifying flue gas | |
| TWI355289B (en) | Method of removing mercury from flue gas after com | |
| CN110642271A (en) | Device and method for melting treatment and refining of industrial waste salt | |
| JP4210456B2 (en) | Cement raw material processing method | |
| KR101835837B1 (en) | Calcium removal method | |
| CN112808746B (en) | Resource treatment method for incineration slag and fly ash | |
| US4873065A (en) | Flue gas purification process | |
| US3890207A (en) | Air and water pollution control | |
| US6379639B2 (en) | Process for purification of flue gas | |
| JP3226914B2 (en) | Flue gas cleaning method | |
| JP2965617B2 (en) | Purification method of waste gas with high chloride content | |
| JPH10314530A (en) | Method for purifying gas loaded with dust | |
| JPH0140680B2 (en) | ||
| JPH11207146A (en) | Method for recovering gypsum from flue gas desulfurization wastewater | |
| JPH04504378A (en) | Method for purifying flue gas generated during garbage incineration | |
| JP2566746B2 (en) | How to clean a flue gas stream | |
| JPH0929058A (en) | Solidification of desulfurized drain with coal ash | |
| JP3727366B2 (en) | Method and apparatus for purifying gases containing sulfur dioxide | |
| JPH07187660A (en) | Recovery of ammonia from flue gas residual dross | |
| KR100315698B1 (en) | Improved method for heat treating flue gas purification residues and residues obtained from industrial processes generating the flue gas | |
| JP6127113B1 (en) | Radioactive contaminant treatment method and radioactive contaminant treatment facility | |
| JPH05285335A (en) | High-performance comprehensive exhaust gas treatment method | |
| JP3295935B2 (en) | Wet exhaust gas desulfurization equipment |