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JP3602328B2 - Method and apparatus for recovering chlorine from shredder dust - Google Patents
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JP3602328B2 - Method and apparatus for recovering chlorine from shredder dust - Google Patents

Method and apparatus for recovering chlorine from shredder dust Download PDF

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JP3602328B2
JP3602328B2 JP07670798A JP7670798A JP3602328B2 JP 3602328 B2 JP3602328 B2 JP 3602328B2 JP 07670798 A JP07670798 A JP 07670798A JP 7670798 A JP7670798 A JP 7670798A JP 3602328 B2 JP3602328 B2 JP 3602328B2
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Prior art keywords
calcium chloride
shredder dust
solution
gypsum
concentration
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JPH11253747A (en
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実 飛田
伸宏 喜原
信義 加賀山
圭史 武正
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Dowa Holdings Co Ltd
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Dowa Holdings Co Ltd
Dowa Mining Co Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は廃自動車、廃家電および建設廃材等のシュレッダーダストの処理方法に関し、特にシュレッダーダストに含まれる塩素分の回収方法に関する。
【0002】
【従来の技術】
自動車部品、家電製品および建設廃材等の固形廃棄物を、材料別でみると、鉄系金属、非鉄系金属、プラスチック、セラミックス等によるいろいろな部材が使われている。シュレッダー処理により、これらの部材が破砕され分解されたときに発生するシュレッダーダストでは、前記のいろいろな材料がいろいろな形で接合されあるいは複合されている。このようなシュレッダーダストについては、金属材料の再資源化のため、プラスチック等有機物や可燃性無機物を焼却し、その焼却残渣から、磁力選別により鉄系金属の回収が行われており、また、非鉄系金属についても、いろいろな回収手段が試みられている。
【0003】
ところで、前記のシュレッダーダストには、有機物として多量のプラスチックが含まれており、現況では、このプラスチックとしては塩素を含有するポリ塩化ビニルが最も多く含まれている。従って、シュレッダーダストの焼却処理においては、その過程で直接的には排ガス中に塩素乃至塩化水素が発生するため、後処理工程として石灰乳による排ガス洗浄が必要であると共に、発生塩素が関与して非常に毒性が強く且つ安定なダイオキシン類を生成することがあり、これが大気中に排出されることは、一般環境汚染の面から極めて深刻な問題をもたらすものとなっており、シュレッダーダストの焼却において大きな障害になっている状況にある。
【0004】
一方、塩素を有用成分とし且つ安定的に含むカルシウム化合物として、塩化カルシウムがある。この塩化カルシウムについては、食塩と炭酸カルシウム(石灰石)を原料として炭酸ソーダを製造するアンモニアソーダ法において、副産物として回収する方法が知られている。即ち、飽和食塩水にアンモニアと二酸化炭素を順次反応させ、炭酸ソーダの母体となる炭酸水素ナトリウムを晶出させて回収した後、この分離後の母液に石灰乳を加えて塩化カルシウムを生成させ、その濃縮過程において食塩を除去し、放冷により固形塩化カルシウムを得る方法である。
【0005】
【発明が解決しようとする課題】
しかしながら、この従来の方法において、シュレッダーダストの焼却過程において発生する塩素乃至塩化水素ガスの有効回収方法がなく、シュレッダーダストを焼却して生成した排ガスを洗浄した洗浄液は、重金属などの不純物を多く含んでいるため、アンモニアソーダ法に準じた方法では高品位の塩化カルシウムを得ることはできない。さらに、当該洗浄液は塩素濃度が低いため、加熱濃縮のための膨大な熱エネルギーを必要とする等、経済性に問題があった。また、シュレッダーダストには、硫黄も含まれており、焼却による燃焼排ガスには、二酸化硫黄が含まれている。従って、塩素ガス乃至塩化水素ガスの吸収や塩化カルシウム液の濃縮時には石膏スケールの生成混入が避けられず、この石膏が設備を閉塞して作業性を著しく妨げるという問題があった。さらに、燃焼排ガスには重金属も含まれ、これが石膏と共に塩化カルシウムの精製を妨げるという問題があった。
【0006】
本発明は、このような問題に鑑み、シュレッダーダストを焼却して有用金属等の資源を回収する処理にあたり、アンモニア性ソーダ液を要することなく、シュレッダーダストの燃焼ガスに含まれる二酸化硫黄や重金属を分離回収すると共に、同時に含まれる塩化水素態の塩素を安全で且つ再資源として利用可能な精製塩化カルシウム化合物の形で、新たな熱エネルギーを消費することなく経済的に濃縮固定化できる効率的な処理方法及び装置の提供を目的とする。
【0007】
【課題を解決するための手段】
上記の目的を達成するため、本発明は、シュレッダーダストを焼却し、燃焼排ガスを濃縮塔内において中和タンクとの間を循環する炭酸カルシウム乳液からなる吸収液に接触させ、該燃焼排ガス中の塩化水素と二酸化硫黄を吸収させて塩化カルシウムと石膏を生成させ、且つ、前記吸収液中の塩化カルシウムの濃度を高めて生成石膏の溶解度を低減させることにより該石膏を優先除去して高濃度塩化カルシウム溶液を得、該高濃度塩化カルシウム溶液に硫化剤を添加して含有金属を硫化物として分離し、次いで、焼却炉の排熱を利用して、塩化カルシウム溶液を濃縮することにより、固形塩化カルシウムを得るところのシュレッダーダストからの塩素回収方法を提供する。
【0008】
さらにまた、シュレッダーダストを焼却する焼却炉と、該焼却炉からの排ガスを燃焼させる燃焼炉と、該燃焼炉からの燃焼排ガスを導入して炭酸カルシウム乳液からなる吸収液と接触させて塩化カルシウムを生成させ且つ濃縮化させる濃縮塔と、該濃縮塔との間で前記吸収液を循環させる中和タンクと、該中和タンクから抽出した濃縮液から石膏を分離除去する遠心分離機と、該遠心分離機からの分離液を受け入れ硫化剤と反応させて金属硫化物を沈殿させる硫化タンクと、該硫化タンクからの前記金属硫化物を濾過分離する濾過機と、該濾過機からの濾液を焼却炉の排熱を利用し、濃縮して塩化カルシウムを析出させる析出凝縮器と、該析出凝縮器からの析出塩化カルシウムを分離回収する濾過装置とを備えてなるシュレッダーダストからの塩素回収装置を提供する。
【0009】
【発明の実施の形態】
本発明は、シュレッダーダストを焼却することによって生じた高温度燃焼排ガスの熱エネルギーを利用し、塩化カルシウムの生成工程において、炭酸カルシウムから石灰乳を得ると共に、この石灰乳に燃焼排ガス中の塩化水素態の塩素を直接的に反応させて塩化カルシウムを得、且つ、この塩化カルシウムを濃縮できるようにしたものであり、その際石膏による設備の閉塞を防止するために、塩化カルシウムを400g/l、石膏を300g/lとし、また、石膏分離後の高濃度塩化カルシウム溶液に含まれている重金属は硫化物として除去することができる。
【0010】
さらに、本発明の実施の形態について、図1のフローシートにより具体的に説明する。
【0011】
シュレッダーダストの焼却炉としてロータリーキルンを使用することにより多量のシュレッダーダストを処理できる。重油等補助燃料を用いて燃焼させ、有機物等自体の燃焼熱を利用して800℃以上にシュレッダーダストを加熱して焼却する。焼却残渣については金属分の再資源化回収のため、別途物理選別工程に供給する。
【0012】
この焼却による排ガスには、未燃焼状態の炭化水素ガス等が含まれているので、さらに、補助燃料を使用して二次燃焼炉乃至三次燃焼炉において、完全燃焼を図り、燃焼排ガスとする。
【0013】
塩化水素ガスや二酸化炭素ガス等を含む燃焼排ガスを、濃縮塔に導入し、含まれている塩化水素ガスを吸収液と接触させる。この吸収液は、石膏が過飽和の状態になるとポンプや配管内にスケールとなり閉塞しやすいため、石膏を飽和以上に懸濁させたスラリー状溶液であって、中和タンクと濃縮塔との間を循環させる。さらに、この石膏は塩化カルシウムとの共存下において、塩化カルシウムの濃度に応じて溶解度が減少する性質があるため、石膏が過飽和になりにくくなりトラブルを防止することができる。石膏は中和タンクへの炭酸カルシウムの添加と排ガス中に含まれる二酸化硫黄との反応熱により効率的に補給される。炭酸カルシウムは安価に入手し易い原料でもある。濃縮塔における高温度の燃焼排ガスとの接触により、塩化水素ガスは90%以上吸収されカルシウムと反応して塩化カルシウムを生成する。吸収液は循環中に継続的に塩化カルシウムを生成して濃縮化される。
【0014】
濃縮塔でカルシウム化合物からなる吸収液と接触させ、塩化水素ガスを分離し且つ冷却した燃焼排ガスを高次洗浄塔に送り、苛性ソーダ水溶液で十分に洗浄した後、ダスト類を電気集塵機により除去し無害化して清浄ガスとして煙突から大気中に放出する。
【0015】
一方、循環する吸収液は前記のように塩化カルシウムで濃縮化された溶液となり中和タンク底部に濃縮液を滞留する。また、吸収液は燃焼排ガス中の硫黄酸化物とも反応して石膏を生成し、石膏が濃縮化する。この石膏は析出することにより、循環ポンプや配管等を閉塞するようになる。従って、中和タンクから適宜濃縮液を抽出し、析出した石膏と共に濃縮液を適宜抽出し、遠心分離機に導入することにより固液分離して石膏を分離することができる。なお、この滞留濃縮液は中和タンクへの新たな吸収液乃至炭酸カルシウムの供給量に見合った量が抽出され、循環量が保てるようにする。
【0016】
分離液即ち高濃度塩化カルシウム液は、塩化カルシウムの他に、銅、鉛、亜鉛等重金属等を不純物として含んでいる。この高濃度塩化カルシウム液を硫化タンクに導入し、硫化剤として反応性がよく入手し易い硫化ソーダを添加して反応させることにより、前記重金属を難溶性の金属硫化物として沈殿させることができ、この金属硫化物を含む高濃度塩化カルシウム液をフィルタプレス等濾過機に掛けることにより、金属硫化物を濾過分離することができる。この金属硫化物は亜鉛品位が高く、亜鉛製錬原料としてリサイクル可能である。
【0017】
さらに、この濾液は塩化ナトリウムを含有した高濃度塩化カルシウム溶液であり、この溶液を電気的加熱をおこなう析出凝縮器において、溶液を凝縮することにより塩化ナトリウムを凝縮的に且つ十分に晶出させることができる。また、この固液混合液を濾過機に掛けることにより固体塩化ナトリウムを分離回収することができ、得られた高濃度塩化カルシウム濾液をさらに濃縮晶出させることにより固体塩化カルシウムが回収できる。この固定塩化カルシウムは、JIS K8124(乾燥用)、8125(水分測定用)の規定を満足する純度の塩化カルシウム二水塩である。塩化カルシウムを回収した後の濾液は吸収液の母液として循環利用することができる。
【0018】
【実施例】
以下、シュレッダーダストを対象に図1のフローシートの方法および装置に従って処理し、シュレッダーダスト燃焼排ガス吸収液から塩化カルシウム生成までの各工程における生成物について調査した。
【0019】
即ち、表1の性状に代表されるシュレッダーダストをシュレッダーダスト自体に多く含まれる有機物の燃焼熱を利用してロータリーキルン中で重油等補助燃料を用い800℃以上に加熱焼却した。
【0020】
排ガス中には未燃焼状態の炭化水素ガス等が含まれ、これを二次燃焼炉、三次燃焼炉において補助燃料を用い、完全燃焼させ燃焼排ガスとした。
【0021】
塩化水素ガスや二酸化硫黄ガス等を含む燃焼排ガスをキャスターライニングしたSS製ダクト(内径350mm)からSUS316製濃縮塔(内径350mm、長さ9500mm)の急冷部(カーボン管)に導入し、含まれている塩化水素ガスをコアレス型スプレーノズルで噴霧されている吸収液と接触させる。このとき、排熱による吸収液中の水分の蒸発および循環している中和タンクでの炭酸カルシウムの添加により、液中のカルシウム、塩素濃度はそれぞれ150g/l、200〜300g/l程度まで濃縮される。
【0022】
この濃縮液を280L抜き出し、脱石膏工程即ち、堅型、固形分下抜出、手動かき取り式遠心分離機に導入し、排ガス中のSO から生成した(CaSO )を100kg液中から分離した。
【0023】
分離液240LはテフロンライニングしたSUS316L製濾液クッションタンクに溜められ、次工程の硫化工程に送られる。
【0024】
テフロンライニングしたSUS316L型硫化タンクにおいて、該分離機に対して0.67kgの硫化ソーダを添加し、反応後、手動開閉式濾過面積0.96m のフィルタープレスで濾過し、10kgの硫化殿物を得た。
【0025】
濾液即ち高濃度塩化カルシウム溶液200Lは上部開放型の析出電気炉上の析出鍋で加熱濃縮した。
【0026】
濃縮が進むと塩化ナトリウムがまず析出する。塩化カルシウムが溶液中で40wt%になった時点、本試験では液量が150Lで加熱を一時止め、塩化ナトリウムを磁性ロート型の濾過機で分離した。
【0027】
濾液は再度、析出電気炉上で加熱濃縮され、残り8L程度で加熱を止め析出した塩化カルシウムと濾液を前記濾過器で濾別して回収する。
【0028】
以上、濃縮液から塩化カルシウム生成までの一連の中間製品、各工程液のカルシウム濃度、塩素濃度を測定した結果およびカルシウム、塩素の物量を表2に示した。
【0029】
また、硫化工程で得られる硫化殿物の各成分の分析値を表3に、最終製品として得られた塩化カルシウムの品位を表4に示す。
【0030】
【表1】

Figure 0003602328
【0031】
【表2】
Figure 0003602328
【0032】
【表3】
Figure 0003602328
【0033】
【表4】
Figure 0003602328
【0034】
【発明の効果】
本発明によれば、シュレッダーダストを焼却して有用金属等の資源を回収するにあたり、その焼却排ガスに含まれる塩化水素態の塩素を排ガスの持つ燃焼熱を利用して、好ましくは入手し易い炭酸カルシウムの添加による石灰乳からなる吸収液と反応させて塩化カルシウムとすることができ、また、前記吸収液を循環的に燃焼排ガスと接触させることにより濃縮的に塩化カルシウム液を生成させることができ、燃焼排ガスに同時に含まれる硫黄分を石膏として、重金属を硫化物としてそれぞれ除去し、安全で、且つ、JIS規定を満足する精製塩化カルシウム製造できるものであって、効率的に、従って経済的に回収できる比較的簡単な方法及び装置を提供できるという効果を奏するものである。
【図面の簡単な説明】
【図1】本発明のシュレッダーダストの焼却によって発生する排ガスから塩化カルシウムを生成するための工程を示すフローシートである。[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method for treating shredder dust from waste automobiles, waste home appliances, construction waste materials, and the like, and more particularly, to a method for recovering chlorine contained in shredder dust.
[0002]
[Prior art]
When looking at solid waste such as automobile parts, home appliances and construction waste materials by material, various members made of ferrous metals, non-ferrous metals, plastics, ceramics, and the like are used. In shredder dust generated when these members are crushed and decomposed by shredder treatment, the above-mentioned various materials are bonded or combined in various forms. For such shredder dust, in order to recycle metal materials, organic substances such as plastics and flammable inorganic substances are incinerated, and ferrous metals are collected from the incineration residue by magnetic separation, and non-ferrous metals. Various recovery methods have also been attempted for system metals.
[0003]
By the way, the above-mentioned shredder dust contains a large amount of plastic as an organic substance, and at present, polyvinyl chloride containing chlorine is most contained as this plastic. Therefore, in the incineration treatment of shredder dust, chlorine or hydrogen chloride is directly generated in the exhaust gas in the process, so that it is necessary to clean the exhaust gas with lime milk as a post-treatment step, and the generated chlorine is involved. Very toxic and stable dioxins can be produced, and their release into the air poses a very serious problem in terms of general environmental pollution. The situation is a major obstacle.
[0004]
On the other hand, calcium chloride is a calcium compound containing chlorine as a useful component and stably. It is known that calcium chloride is recovered as a by-product in the ammonia soda method for producing sodium carbonate using salt and calcium carbonate (limestone) as raw materials. That is, ammonia and carbon dioxide are sequentially reacted with saturated saline to crystallize and recover sodium bicarbonate, which is the base of sodium carbonate, and then, to the separated mother liquor, lime milk is added to generate calcium chloride, This is a method in which salt is removed during the concentration process, and solid calcium chloride is obtained by standing to cool.
[0005]
[Problems to be solved by the invention]
However, in this conventional method, there is no effective method for recovering chlorine or hydrogen chloride gas generated in the incineration process of shredder dust, and the cleaning solution for cleaning exhaust gas generated by incineration of shredder dust contains many impurities such as heavy metals. Therefore, high-grade calcium chloride cannot be obtained by a method based on the ammonia soda method. Further, since the cleaning solution has a low chlorine concentration, there is a problem in economical efficiency, such as requiring a huge amount of heat energy for heat concentration. Shredder dust also contains sulfur, and combustion exhaust gas from incineration contains sulfur dioxide. Therefore, there is a problem that gypsum scale is inevitably generated and absorbed at the time of absorption of chlorine gas or hydrogen chloride gas and concentration of calcium chloride solution, and this gypsum obstructs equipment and remarkably hinders workability. Further, there is a problem that the combustion exhaust gas also contains heavy metals, which hinder the purification of calcium chloride together with gypsum.
[0006]
In view of such a problem, the present invention eliminates the need for ammoniacal soda solution in the process of incinerating shredder dust and recovering resources such as useful metals, and eliminates sulfur dioxide and heavy metals contained in the combustion gas of shredder dust. Efficient separation and recovery, and efficient enrichment and immobilization of hydrogen chloride chlorine contained simultaneously in the form of a purified calcium chloride compound that is safe and can be reused without consuming new heat energy It is intended to provide a processing method and an apparatus.
[0007]
[Means for Solving the Problems]
In order to achieve the above object, the present invention incinerates shredder dust, makes the combustion exhaust gas come into contact with an absorbent consisting of calcium carbonate emulsion circulating between a neutralization tank in a concentration tower, By absorbing hydrogen chloride and sulfur dioxide to form calcium chloride and gypsum, and by increasing the concentration of calcium chloride in the absorbing solution to reduce the solubility of the formed gypsum, the gypsum is preferentially removed to obtain a high concentration chloride. A calcium solution is obtained, a sulfurizing agent is added to the high-concentration calcium chloride solution to separate contained metals as sulfides, and then the wastewater from the incinerator is used to concentrate the calcium chloride solution to obtain a solid chloride. A method for recovering chlorine from shredder dust for obtaining calcium is provided.
[0008]
Furthermore, an incinerator for incinerating shredder dust, a combustion furnace for burning exhaust gas from the incinerator, and a flue gas from the combustion furnace are introduced and brought into contact with an absorbent comprising calcium carbonate latex to form calcium chloride. A concentration tower for generating and concentrating, a neutralization tank for circulating the absorbing solution between the concentration tower, a centrifuge for separating and removing gypsum from the concentrated solution extracted from the neutralization tank, A sulfide tank for receiving the separated liquid from the separator and reacting with a sulfide agent to precipitate metal sulfide, a filter for filtering and separating the metal sulfide from the sulfide tank, and an incinerator for filtering the filtrate from the filter. From the shredder dust comprising a precipitation condenser for concentrating and precipitating calcium chloride by utilizing the exhaust heat of, and a filtration device for separating and recovering the precipitated calcium chloride from the precipitation condenser. To provide a chlorine recovery system.
[0009]
BEST MODE FOR CARRYING OUT THE INVENTION
The present invention utilizes thermal energy of high-temperature flue gas generated by incineration of shredder dust to obtain lime milk from calcium carbonate in a calcium chloride producing step, and to add lime milk to hydrogen chloride in flue gas in the flue gas. Is to directly react the chlorine in the form to obtain calcium chloride and to concentrate the calcium chloride. In order to prevent clogging of the equipment with gypsum, 400 g / l of calcium chloride is used. The gypsum is set to 300 g / l, and heavy metals contained in the high-concentration calcium chloride solution after the separation of gypsum can be removed as sulfide.
[0010]
Further, an embodiment of the present invention will be specifically described with reference to a flow sheet of FIG.
[0011]
A large amount of shredder dust can be treated by using a rotary kiln as an incinerator for shredder dust. The fuel is burned using an auxiliary fuel such as heavy oil, and the shredder dust is heated to 800 ° C. or more and incinerated using the combustion heat of the organic matter itself. The incineration residue is separately supplied to the physical separation process for recycling and collecting metal.
[0012]
Since the exhaust gas from this incineration contains hydrocarbon gas and the like in an unburned state, the secondary combustion furnace or the tertiary combustion furnace further uses an auxiliary fuel to complete combustion to produce combustion exhaust gas.
[0013]
Combustion exhaust gas containing hydrogen chloride gas, carbon dioxide gas, and the like is introduced into the concentration tower, and the contained hydrogen chloride gas is brought into contact with the absorbing solution. When the gypsum becomes supersaturated, the absorption liquid becomes a scale in a pump or a pipe and is easily clogged. Circulate. Furthermore, since this gypsum has a property that the solubility decreases in accordance with the concentration of calcium chloride in the coexistence with calcium chloride, the gypsum is less likely to be supersaturated, and troubles can be prevented. Gypsum is efficiently replenished by the addition of calcium carbonate to the neutralization tank and the heat of reaction with the sulfur dioxide contained in the exhaust gas. Calcium carbonate is also an inexpensive raw material. Due to the contact with the combustion exhaust gas at a high temperature in the concentration tower, hydrogen chloride gas is absorbed by 90% or more and reacts with calcium to generate calcium chloride. The absorption liquid continuously concentrates by producing calcium chloride in the circulation.
[0014]
After being brought into contact with an absorption solution consisting of a calcium compound in a concentration tower, hydrogen chloride gas is separated, and the cooled combustion exhaust gas is sent to a high-order washing tower, which is sufficiently washed with an aqueous solution of caustic soda. And emits it as a clean gas from the chimney into the atmosphere.
[0015]
On the other hand, the circulating absorbent becomes a solution concentrated with calcium chloride as described above, and the concentrated liquid stays at the bottom of the neutralization tank. Further, the absorbing liquid also reacts with sulfur oxides in the combustion exhaust gas to form gypsum, and the gypsum is concentrated. The gypsum precipitates and blocks a circulation pump, piping, and the like. Therefore, the concentrated liquid is appropriately extracted from the neutralization tank, the concentrated liquid is appropriately extracted together with the precipitated gypsum, and introduced into a centrifugal separator, whereby the gypsum can be separated by solid-liquid separation. In addition, this retained concentrated liquid is extracted in an amount corresponding to the supply amount of the new absorption liquid or calcium carbonate to the neutralization tank so that the circulation amount can be maintained.
[0016]
The separation liquid, that is, the high-concentration calcium chloride liquid contains, in addition to calcium chloride, heavy metals such as copper, lead, and zinc as impurities. The heavy metal can be precipitated as a hardly soluble metal sulfide by introducing this high-concentration calcium chloride solution into a sulfidation tank and adding and reacting sodium sulfide, which is easily reactive and easily available as a sulfidizing agent, The metal sulfide can be filtered and separated by applying the high-concentration calcium chloride solution containing the metal sulfide to a filter such as a filter press. This metal sulfide has a high zinc quality and can be recycled as a zinc smelting raw material.
[0017]
Further, the filtrate is a high-concentration calcium chloride solution containing sodium chloride, and this solution is condensed and sufficiently crystallized by condensing the solution in a precipitation condenser for electrically heating the solution. Can be. In addition, solid sodium chloride can be separated and recovered by applying the solid-liquid mixture to a filter, and solid calcium chloride can be recovered by further concentrating and crystallizing the obtained high-concentration calcium chloride filtrate. The fixed calcium chloride is a calcium chloride dihydrate having a purity satisfying JIS K8124 (for drying) and 8125 (for moisture measurement). The filtrate after recovering the calcium chloride can be circulated and used as a mother liquor of the absorbing solution.
[0018]
【Example】
Hereinafter, the shredder dust was treated according to the method and apparatus of the flow sheet of FIG. 1 and the products in each step from the shredder dust combustion exhaust gas absorbing solution to the formation of calcium chloride were investigated.
[0019]
That is, shredder dust typified by the properties shown in Table 1 was incinerated by heating at 800 ° C. or more in a rotary kiln by using auxiliary fuel such as heavy oil by utilizing the heat of combustion of organic substances contained in the shredder dust itself.
[0020]
The exhaust gas contains unburned hydrocarbon gas and the like, which was completely burned in a secondary combustion furnace and a tertiary combustion furnace using an auxiliary fuel to obtain a combustion exhaust gas.
[0021]
Combustion exhaust gas containing hydrogen chloride gas, sulfur dioxide gas, etc. is introduced from a caster-lined SS duct (inner diameter 350 mm) into a quenching section (carbon pipe) of a SUS316 concentration tower (inner diameter 350 mm, length 9500 mm) and contained. The hydrogen chloride gas is brought into contact with the absorbing solution sprayed by the coreless spray nozzle. At this time, the concentration of calcium and chlorine in the liquid is concentrated to about 150 g / l and about 200 to 300 g / l, respectively, by evaporating the water in the absorbing liquid by the exhaust heat and adding calcium carbonate in the circulating neutralization tank. Is done.
[0022]
280 L of this concentrated solution was withdrawn, and the degaypsum process was performed, that is, a solid, withdrawn under solid content, and introduced into a manual scraping-type centrifuge, and 100 kg of (CaSO 4 ) produced from SO 2 in the exhaust gas was separated from the solution. did.
[0023]
The separated solution (240 L) is stored in a Teflon-lined SUS316L filtrate cushion tank and sent to the subsequent sulfurization step.
[0024]
In a SUS316L type sulfurizing tank lined with Teflon, 0.67 kg of sodium sulfide was added to the separator, and after the reaction, the mixture was filtered with a manually openable filter press having a filter area of 0.96 m 2 to remove 10 kg of sulfurized residue. Obtained.
[0025]
The filtrate, that is, 200 L of a high concentration calcium chloride solution was heated and concentrated in a precipitation pot on a deposition electric furnace having an open top.
[0026]
As the concentration proceeds, sodium chloride precipitates first. In this test, when the calcium chloride became 40 wt% in the solution, heating was temporarily stopped at a liquid volume of 150 L, and sodium chloride was separated by a magnetic funnel type filter.
[0027]
The filtrate is again concentrated by heating on a deposition electric furnace, and the heating is stopped at about the remaining 8 L, and the precipitated calcium chloride and the filtrate are separated and collected by the filter.
[0028]
As described above, Table 2 shows a series of intermediate products from the concentrated solution to the formation of calcium chloride, the results of measuring the calcium concentration and the chlorine concentration of each process solution, and the amounts of calcium and chlorine.
[0029]
Table 3 shows the analytical values of the components of the sulfurized residue obtained in the sulfurization step, and Table 4 shows the grade of calcium chloride obtained as the final product.
[0030]
[Table 1]
Figure 0003602328
[0031]
[Table 2]
Figure 0003602328
[0032]
[Table 3]
Figure 0003602328
[0033]
[Table 4]
Figure 0003602328
[0034]
【The invention's effect】
According to the present invention, in recovering resources such as useful metals by incineration of shredder dust, hydrogen chloride chlorine contained in the incineration exhaust gas is utilized by utilizing the combustion heat of the exhaust gas, and carbon dioxide is preferably easily available. It can be reacted with an absorbing solution composed of lime milk by adding calcium to form calcium chloride, and the absorbing solution can be concentrated and produced by contacting the absorbing solution with combustion exhaust gas in a concentrated manner. It removes sulfur contained in the combustion exhaust gas simultaneously as gypsum and heavy metals as sulfides, and can produce purified calcium chloride that is safe and satisfies JIS regulations. This has the effect of providing a relatively simple method and apparatus that can be recovered.
[Brief description of the drawings]
FIG. 1 is a flow sheet showing a process for producing calcium chloride from exhaust gas generated by incineration of shredder dust of the present invention.

Claims (2)

シュレッダーダストを焼却し、燃焼排ガスを濃縮塔内において中和タンクとの間を循環する炭酸カルシウム乳液からなる吸収液に接触させ、該燃焼排ガス中の塩化水素と二酸化硫黄を吸収させて塩化カルシウムと石膏を生成させ、且つ、前記吸収液中の塩化カルシウムの濃度を高めて生成石膏の溶解度を低減させることにより該石膏を優先除去して高濃度塩化カルシウム溶液を得、該高濃度塩化カルシウム溶液に硫化剤を添加して含有金属を硫化物として分離し、加熱凝縮して固形塩化カルシウムを得ることを特徴とするシュレッダーダストからの塩素回収方法。The shredder dust is incinerated, and the flue gas is brought into contact with an absorbent consisting of calcium carbonate latex circulating between the neutralization tank in the concentration tower to absorb hydrogen chloride and sulfur dioxide in the flue gas to form calcium chloride. Gypsum is produced, and the concentration of calcium chloride in the absorbing solution is increased to reduce the solubility of the produced gypsum, thereby preferentially removing the gypsum to obtain a high-concentration calcium chloride solution. A method for recovering chlorine from shredder dust, comprising adding a sulfurizing agent to separate contained metals as sulfides, and condensing by heating to obtain solid calcium chloride. シュレッダーダストを焼却する焼却炉と、該燃焼炉からの燃焼排ガスを導入して炭酸カルシウム乳液からなる吸収液と接触させて塩化カルシウムを生成し且つ濃縮化する濃縮塔と、該濃縮塔との間で前記吸収液を循環させる中和タンクと、該中和タンクから抽出した濃縮液から石膏を分離除去する遠心分離機と、該遠心分離機からの分離液を受け入れ硫化剤と反応させて金属硫化物を沈殿させる硫化タンクと、該硫化タンクからの前記金属硫化物を濾過分離する濾過機と、該濾過機からの濾液を加熱濃縮し塩化カルシウムを析出させる析出凝縮器と、該析出凝縮器からの析出塩化カルシウムを分離回収する濾過装置とを備えてなることを特徴とするシュレッダーダストからの塩素回収装置。An incinerator for incinerating the shredder dust, a concentrating tower for introducing the flue gas from the combustion furnace and bringing it into contact with an absorbing solution comprising calcium carbonate emulsion to generate and concentrate calcium chloride, and A neutralizing tank for circulating the absorbing solution, a centrifuge for separating and removing gypsum from the concentrated solution extracted from the neutralizing tank, and receiving the separated solution from the centrifugal separator and reacting it with a sulfurizing agent to form a metal sulfide. A sulfide tank for precipitating matter, a filter for filtering and separating the metal sulfide from the sulfide tank, a precipitation condenser for heating and concentrating a filtrate from the filter to precipitate calcium chloride, and And a filtration device for separating and recovering calcium chloride precipitated from the shredder dust.
JP07670798A 1998-03-10 1998-03-10 Method and apparatus for recovering chlorine from shredder dust Expired - Lifetime JP3602328B2 (en)

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