JPH07185034A - Method for treating industrial waste, and treating agent - Google Patents

Method for treating industrial waste, and treating agent

Info

Publication number
JPH07185034A
JPH07185034A JP5355252A JP35525293A JPH07185034A JP H07185034 A JPH07185034 A JP H07185034A JP 5355252 A JP5355252 A JP 5355252A JP 35525293 A JP35525293 A JP 35525293A JP H07185034 A JPH07185034 A JP H07185034A
Authority
JP
Japan
Prior art keywords
fatty acid
quick lime
industrial waste
silicate
slag
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
Application number
JP5355252A
Other languages
Japanese (ja)
Inventor
Toshio Yamamoto
利夫 山本
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP5355252A priority Critical patent/JPH07185034A/en
Publication of JPH07185034A publication Critical patent/JPH07185034A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To stabilize the oil, heavy metal and the like in an industrial waste to allow a safety waste treatment by adding and kneading each treating agent consisting of fatty acid, quick lime, silicate and the like to the industrial waste containing the oil, liquid organic chlorine compound, and heavy metal, and mixing water thereto to react them. CONSTITUTION:To an industrial waste containing oil or liquid organic chlorine compound, and heavy metal which is put in a mixer, the same quantity or more of a treating agent consisting of about 85%-93% of quick lime, about 5%-2% of fatty acid, and about 10%-5% of silicate, or a treating agent consisting of about 65%-35% of quick lime, about 5%-2% of fatty acid, and about 30%-63% of slag dust is added, and mixed therewith. Thereafter, a necessary quantity of water is mixed thereto followed by stirring to make the industrial waste contain it, whereby the oil, liquefied organic chlorine compound such as liquid organic halogen compound, and heavy metal are solidified. The solid composition is covered with and fixed to asphalt so that the oil or liquefied organic chlorine compound contained in the industrial waste are not eluted.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は主として産業廃棄物に含
有する油分、テトラクロロエチレン及び液体PCB又は
銅、クロム、鉛、水銀、カドミニウム、シアン、砒素等
の重金属を固定し安全な廃棄物としてその廃棄処理を可
能とする産業廃棄物の処理方法及びその処理剤に関す
る。
BACKGROUND OF THE INVENTION The present invention mainly fixes oil contained in industrial waste, tetrachloroethylene and liquid PCB or heavy metals such as copper, chromium, lead, mercury, cadmium, cyanide and arsenic, and disposes them as safe waste. The present invention relates to a method for treating industrial waste that enables treatment and a treating agent therefor.

【0002】[0002]

【従来の技術】従来、化学工場、バルブ工場、IC生産
工場、機械工場、製鉄所等から排出される産業廃棄物の
中には油分、有機塩素化合物及び有害重金属が混入した
りして、これらをそのまま廃棄すると、土壌、河川、海
等の環境破壊を生ずるという問題があった。そこで従来
は、油分、液体有機塩素化合物及び汚染土壌は焼却し、
重金属を含む場合はセメント等の適当な固化剤を混入し
て、廃棄物を固化させ該固化物を廃棄処理することが提
案されていた。又、PCB等液体有機はろげん化物は非
常に安定な化合物であり、しかも有害性を有するから、
その廃棄処分には非常な困難が伴う、現在、液状PCB
を保有する企業の一部では、使用禁止となった当初、暫
定的な処理として、ドラム缶或るいはトランス等に保有
のまま保管されてきた、これらは適正な処理がなされな
いまま長年月を経て、容器の腐食から漏出したり、放置
したトランスから洩れたりすることが起きており、極め
て憂慮すべき状態である。現在PCBは焼却によって処
理されているが、焼却に際し極めて高い温度1100℃
以上が必要とされ不完全燃焼するとダイオキシン類が発
生して二次汚染するなど処理に困難が伴っている。
2. Description of the Related Art Conventionally, oil, organic chlorine compounds and harmful heavy metals are mixed in industrial waste discharged from chemical factories, valve factories, IC production factories, machine factories, steel mills, etc. However, there is a problem that if it is discarded as it is, the environment such as soil, river and sea will be destroyed. Therefore, conventionally, oil, liquid organic chlorine compounds and contaminated soil are incinerated,
When a heavy metal is contained, it has been proposed to mix an appropriate solidifying agent such as cement to solidify the waste and dispose of the solidified product. In addition, since liquid organic molasses such as PCB is a very stable compound and is harmful,
Currently, liquid PCBs are extremely difficult to dispose of.
At the beginning of the ban on the use, some companies that have been holding the products have kept them in drums, transformers, etc. as provisional processing, and these have been stored for many years without proper processing. However, there are cases where the container leaks due to corrosion or leaks from a transformer that has been left unattended, which is extremely alarming. PCBs are currently processed by incineration, but the extremely high temperature of 1100 ℃
If the above is required and incomplete combustion occurs, dioxins are generated and secondary pollution occurs, which makes processing difficult.

【0003】[0003]

【発明が解決しようとする課題】しかしながら従来の例
に係わる産業廃乗物の処理方法において、産業廃棄物を
焼却処理する場合には、大型の焼却炉が必要で莫大な経
費がかかっていた。又、産業廃棄物中に重金属を含む場
合には、その処理が複雑で困難を伴っていた。本発明は
このような事情に鑑みなされたもので、産業廃棄物に含
まれる油分又は液体有機ハロゲン化合物及び重金属を固
定化し、又は固定化したその固定物粒子を被覆固定する
ことによって溶出を難しくする産業廃棄物の処理方法及
びその処理剤を提供することを目的とする。
However, in the industrial waste vehicle treatment method according to the conventional example, when incinerating the industrial waste, a large incinerator is required and a huge cost is required. Further, when heavy metal is contained in industrial waste, its treatment is complicated and difficult. The present invention has been made in view of such circumstances, and makes it difficult to elute by immobilizing oil or liquid organic halogen compounds and heavy metals contained in industrial waste, or by coating and immobilizing the immobilized immobilization product particles. An object of the present invention is to provide a method for treating industrial waste and a treating agent therefor.

【0004】[0004]

【課題を解決するための手段】前記目的に沿う「請求項
1」記載の産業廃棄物の処理方法は、ミキサーに入れた
油分又は液体有機塩素化合物及び重金属を含有する産業
廃棄物に、生石灰85%〜93%脂肪酸5%〜2%珪酸
塩10%〜5%とからなる処理剤、又は、生石灰65%
〜35%脂肪酸5%〜2%鉱滓微粉塵30%〜63%と
からなる処理剤及び生石灰57%〜35%脂肪酸5%〜
2%珪酸塩8%〜3%鉱滓微粉塵30%〜60%からな
る処理剤を同量もしくは同量以上添加して混合し、その
後必要量の水を混入して撹拌し産業廃棄物に含有する、
油分又は液体有機ハロゲン化合物及び重金属を固定する
ように構成されている。前記目的に沿う「請求項2」記
載の産業廃棄物の処理方法は、ミキサーに入れた油分又
は液体有機塩素化合物及び重金属を含有する産業廃棄物
に、生石灰85%〜93%脂肪酸5%〜2%珪酸塩10
%〜5%とからなる処理剤又は、生石灰65%〜35%
脂肪酸5%〜2%鉱滓30%〜63%からなる処理剤及
び生石灰57%〜35%脂肪酸5%〜2%珪酸塩8%〜
3%鉱滓30%〜60%からなる処理剤を同量もしくは
同量以上添加して混合しその後必要量の水を混入して撹
拌放置すると固体状組成物化してこの固体状組成物をア
スファルトで被覆固定して産業廃棄物に含有する油分又
は液状有機塩素化合物及び重金属が溶出しないように構
成されている。前記目的に沿う「請求項3」記載の処理
剤は、生石灰85%〜93%脂肪酸5%〜2%珪酸塩1
0%〜5%とからなるように構成されている。前記目的
に沿う「請求項4」記載の処理剤は、生石灰65%〜3
5%脂肪酸脂肪酸5%〜2%鉱滓微粉塵30%〜63%
とからなるように構成されている。前記目的に沿う「請
求項5」記載の処理剤は、生石灰57%〜35%脂肪酸
脂肪酸5%〜2%珪酸塩8%〜3%鉱滓微粉塵30%〜
60%とからなるように構成されている。前記目的に沿
う「請求項6」記載の処理剤は、生石灰が界面活性を有
し反応を遅らせる物質(生石灰に対し5%〜2%)でコ
ーテイングされることにより「請求項3.4.5」の処
理剤の構成が表1.表2.表3のように変わる。
In order to achieve the above object, the method for treating industrial waste according to the first aspect of the present invention provides a method for treating industrial waste containing oil or liquid organic chlorine compounds and heavy metals in a mixer with quicklime 85. % -93% fatty acid 5% -2% silicate 10% -5%, or lime 65%
~ 35% fatty acid 5% ~ 2% treatment powder consisting of fine slag dust 30% ~ 63% and quick lime 57% ~ 35% fatty acid 5% ~
2% silicate 8% to 3% Fine slag 30% to 60% of the treatment agent is added in the same amount or more and mixed, and then mixed with a necessary amount of water and stirred to be contained in industrial waste To do
It is configured to immobilize oil or liquid organohalogen compounds and heavy metals. According to the method for treating industrial waste according to claim 2, which meets the above-mentioned object, quick lime 85% -93% fatty acid 5% -2 is added to industrial waste containing oil or liquid organic chlorine compound and heavy metal put in a mixer. % Silicate 10
% To 5% or quick lime 65% to 35%
Treatment agent consisting of fatty acid 5% to 2% slag 30% to 63% and quick lime 57% to 35% fatty acid 5% to 2% silicate 8% to
A treatment agent consisting of 30% to 60% of 3% slag is added in the same amount or more than the same amount and mixed, and then a necessary amount of water is mixed and left to stir to form a solid composition, and this solid composition is converted into asphalt. It is configured so that the oil content or liquid organic chlorine compounds and heavy metals contained in industrial waste after being fixed by coating are not eluted. The treating agent according to claim 3 which meets the above-mentioned object is quick lime 85% -93% fatty acid 5% -2% silicate 1
It is composed of 0% to 5%. The treating agent according to "claim 4" according to the above object is quick lime 65% to 3%.
5% Fatty acid Fatty acid 5% to 2% Fine slag dust 30% to 63%
It is configured to consist of and. According to the above-mentioned object, the treating agent according to claim 5 is quicklime 57% -35% fatty acid fatty acid 5% -2% silicate 8% -3% slag fine dust 30%-
And 60%. The treating agent according to "claim 6" which meets the above-mentioned object is coated with a substance (5% to 2% based on quick lime) of quick lime which has a surface activity and delays the reaction. Table 1 shows the composition of the treating agent of ". Table 2. It changes as shown in Table 3.

【0005】[0005]

【作用と実施例】ミキサー内に油分又は液体有機塩素化
合物及び重金属を含有する産業廃棄物と表1.表2.表
3.のいずれかの処理剤を同量もしくは同量以上添加混
合して水を混入し撹拌する。水の量は処理対象物が含有
する水の量によるが含まれてない場合処理剤の30〜5
0重量%の水が適当である。そして生石灰は水との水和
反応により混合物が80℃〜150℃に昇温し消石灰を
生ずる又、産業廃棄物に含まれる水銀カドニウム銅.
鉛.六価クロム等の重金属イオン(以下Mと記載す
る)と処理剤中の珪酸塩(珪酸ソーダ)又は、鉱滓(高
炉水砕スラグの微粉末)が活性して次ぎの反応によって
重金属の珪酸塩を生ずる。 M+NaSiO→ MSiO+ 2Na これによって含有する重金属を取込み不溶化する。そし
て更に生石灰と水との水和で生じた消石灰と珪酸ソーダ
ーが式の如く反応して珪酸カルシウムを生じる。 Ca(OH)+NaSiO → CaSiO
2NaOH これによって生じた珪酸カルシウムは、極めて多孔質な
物質であるので表面積が大きく吸着性に優れ未反応の重
金属等を吸着結合して溶出を防止する。更に前記重金属
の珪酸塩は、マナリック構造を構成しその内部に重金属
イオンは封入されて不活性化すると考えられるので、こ
れらの相乗効果から重金属を強固に固定することとな
る。そして産業廃棄物に油分又は液体有機ハロゲン化物
が含まれる場合には、生成した多孔質の珪酸カルシウム
に吸着される。又、コーテイングされた生石灰は、水と
の反応を遅らせ発熱的に反応することもないから取り扱
いが容易で作業をしやすい、又疎水性廃棄物が水性の多
相系内にあるときこれを吸収する。水性の多相系内に含
有された、又は加えられた水によって有機物の廃棄物を
吸収した生石灰が水酸化カルシウムになり、珪酸塩と反
応して生成した珪酸カルシウムになる反応過程において
有機物質は極めて細く均一に吸収される。界面活性物と
してステアリン酸及びパルミチン酸のような脂肪酸が適
するがパラフィン油のような石油溜分も又適する。又鉱
滓微粉末はガラス化し内部構造は不安定で反応しやすく
結晶化エネルギーを蓄えているので、重金属類と反応し
て重金属の珪酸塩を生成して不溶化する。「請求項2」
記載の処理方法は「請求項1」の処理方法で「請求項
3.4.5.6」の処理剤を使用して処理した産業廃棄
物の、固体状組成物をアスファルトの持つ耐水性、疎水
性、耐候性、熱可塑性などの物理を利用し、処理物粒子
の表面を被覆固定を図ることにより水との接触を妨げ、
難溶化を図るもので、特に完全不溶出の困難な液状PC
B及びCr.Hg.As.Cn等の重金属を不検出す
ることが可能である。又固化物は耐衝撃性が高く、耐浸
出性に優れ、酸、アルカリに対しても安定したものが得
られる。アスファルトは、固体処理物の20%〜30%
重量の液体アスファルトを混合して120℃〜160℃
の温度でよく混練し被覆固定する。又加圧成型すること
により減量化にも寄与する。なお液状PCBの処理には
廃液を利用することが出来るのでそのメリットも大き
い。
[Operations and Examples] Industrial waste containing oil or liquid organic chlorine compounds and heavy metals in the mixer and Table 1. Table 2. Table 3. The same amount or more than the same amount of any one of the treatment agents is mixed and mixed with water and stirred. The amount of water depends on the amount of water contained in the object to be treated.
0% by weight of water is suitable. The lime is a mixture of mercury-cadmium-copper contained in industrial waste, which is produced by hydration reaction with water to raise the temperature of the mixture to 80 ° C to 150 ° C to produce slaked lime.
lead. Heavy metal ions such as hexavalent chromium (hereinafter referred to as M 2 ) and silicate (sodium silicate) or treating slag (fine powder of blast furnace granulated slag) in the treatment agent are activated and the following reaction causes heavy metal silicate. Cause M 2 + Na 2 SiO 3 → MSiO 2 + 2Na + By this, the heavy metal contained is taken in and insolubilized. Further, slaked lime produced by hydration of quick lime and water and sodium silicate react as in the formula to produce calcium silicate. Ca (OH) 2 + Na 2 SiO 3 → CaSiO 2 +
2NaOH Since the calcium silicate generated by this is an extremely porous substance, it has a large surface area and is excellent in adsorptivity, and adsorbs and binds unreacted heavy metals and the like to prevent elution. Further, since it is considered that the heavy metal silicate forms a manic structure and encloses the heavy metal ions therein and inactivates them, the synergistic effect of these synergistically fixes the heavy metal firmly. When the industrial waste contains oil or liquid organic halide, it is adsorbed on the generated porous calcium silicate. In addition, coated quicklime is easy to handle because it does not react exothermically with the reaction with water, and it is easy to work with. It also absorbs hydrophobic waste when it is in an aqueous multiphase system. To do. In the reaction process, quicklime, which absorbs organic waste by the water contained in or added to the aqueous multiphase system, becomes calcium hydroxide and becomes calcium silicate formed by reacting with silicate. Very fine and evenly absorbed. Fatty acids such as stearic acid and palmitic acid are suitable as surface-active substances, but petroleum fractions such as paraffin oil are also suitable. Further, the slag fine powder is vitrified, its internal structure is unstable, and it easily reacts and stores crystallization energy. Therefore, it reacts with heavy metals to form heavy metal silicates and becomes insoluble. "Claim 2"
The treatment method described is the water resistance of an asphalt having a solid composition of an industrial waste treated by the treatment method of "Claim 1" using the treatment agent of "Claim 3.4.5.6", Using physics such as hydrophobicity, weather resistance, and thermoplasticity, the surface of treated particles is covered and fixed to prevent contact with water,
Liquid PC that is difficult to dissolve and is particularly difficult to completely elute
B and Cr 6. Hg. As. It is possible to undetect heavy metals such as Cn. Further, the solidified product has high impact resistance, excellent leaching resistance, and is stable to acids and alkalis. Asphalt is 20% to 30% of solid processed products
120 ℃ ~ 160 ℃ by mixing heavy liquid asphalt
Knead well at the temperature to fix the coating. Also, pressure molding contributes to weight reduction. In addition, since waste liquid can be used for the treatment of liquid PCB, its merit is great.

【0006】[0006]

【実施例1】「請求項3」の処理剤をCaO85%脂肪
酸(ステアリン酸)5%珪酸塩(珪酸ソーダ)10%の
割合で調整した。廃油50gに処理剤100gを入れて
混合した後水を入れ撹拌した8分後106℃、10分後
97℃であった。15分後粉状になった。処理前油分2
7.0wt%が処理後2.3wt%であった。
Example 1 The treating agent of "Claim 3" was prepared in the proportion of CaO 85% fatty acid (stearic acid) 5% silicate (sodium silicate) 10%. 100 g of the treating agent was added to 50 g of waste oil and mixed, and then water was added and stirred. 106 minutes after 8 minutes and 97 degrees after 10 minutes. It became powdery after 15 minutes. Oil before treatment 2
7.0 wt% was 2.3 wt% after the treatment.

【0007】[0007]

【実施例2】「請求項4」の処理剤をCaO65%、ス
テアリン酸5%、鉱滓30%の割合で精製した。塩酸液
50gに処理剤50gを混合して放置した。処理前水銀
59mgが処理後不検出であった。
[Example 2] The treating agent of "claim 4" was refined in the proportions of CaO 65%, stearic acid 5%, and slag 30%. 50 g of the treating agent was mixed with 50 g of the hydrochloric acid solution and left to stand. 59 mg of mercury before treatment was not detected after treatment.

【0008】[0008]

【実施例3】「請求項5」の処理剤をCaO62%、珪
酸ソーダー5%、鉱滓30%ステアリン酸3%の割合で
調整した。廃油25g処理剤50gを混合し水17gを
入れて混ぜた後放置した。12分後94℃、20分後7
0℃の粉状になった。廃油に含まれたテトラクロロエチ
レン11.000mg/lが処理後0.035mg/l
であった。
Example 3 The treating agent of "Claim 5" was adjusted in the proportions of 62% CaO, 5% sodium silicate, 30% slag and 3% stearic acid. Waste oil (25 g), treating agent (50 g) were mixed, water (17 g) was added, and the mixture was allowed to stand. 12 minutes later 94 ° C, 20 minutes later 7
It became powdery at 0 ° C. Tetrachloroethylene 11.000 mg / l contained in waste oil was 0.035 mg / l after treatment
Met.

【0009】[0009]

【実施例4】表1の処理剤を生石灰90%珪酸ソーダー
10%の割合で調整した。廃油50gに処理剤100g
を混合した後水40gを入れて撹拌した後放置した。1
0分後93℃15分後粉状になった。
Example 4 The treating agents shown in Table 1 were prepared in the proportion of quick lime 90% and sodium silicate 10%. 50g of waste oil and 100g of treatment agent
After mixing, 40 g of water was added, and the mixture was stirred and allowed to stand. 1
After 0 minutes, the mixture became powdery at 93 ° C. after 15 minutes.

【0010】[0010]

【実施例5】表1の処理剤を生石灰90%、珪酸ソーダ
ー10%の割合で調整した。CN廃液40gに処理剤を
80g混合し撹拌した。粉状になった処理前のCN2
6.1g/lが処理後5.18ppmになった。
[Example 5] The treatment agents shown in Table 1 were adjusted in a proportion of quick lime 90% and sodium silicate 10%. 80 g of the treating agent was mixed with 40 g of CN waste liquid and stirred. CN2 before treatment in powder form
6.1 g / l was 5.18 ppm after treatment.

【0011】[0011]

【実施例6】表3の処理剤を生石灰65%珪酸ソーダー
5%、鉱滓30%で調整した処理剤に重金属を含んだ水
溶液を同量入れ混合撹拌した後放置、5分後温度98
℃、15分後には粉状であった。
[Example 6] The treating agent of Table 3 was adjusted with 65% quicklime and 5% sodium silicate and 30% of slag, and the same amount of an aqueous solution containing heavy metals was added to the treating agent.
After 15 minutes at ℃, it was powdery.

【0012】[0012]

【実施例7】表3の処理剤を生石灰65%、珪酸ソーダ
ー5%鉱滓30%で調整した。ミキサーにPCB30
g、処理剤90gを入れて混合した後水を30g入れて
撹拌混合した後放置した。8分後96℃、15分後60
℃で粉状になった。処理前液状三塩化PCB100%が
処理後0.014PPMであった。
Example 7 The treating agents shown in Table 3 were prepared using 65% quick lime, 5% sodium silicate and 30% slag. PCB30 in the mixer
and 90 g of the treating agent were added and mixed, 30 g of water was added, and the mixture was stirred and mixed and then allowed to stand. 96 minutes after 8 minutes, 60 after 15 minutes
Powdered at ℃. Pretreatment liquid trichloride PCB 100% was 0.014PPM after treatment.

【0013】[0013]

【実施例8】表3の処理剤をCaO62%珪酸ソーダー
8%鉱滓30%で調製した液体PCB30gに処理理剤
90gを入れて混合した後硫酸銅液34gを入れて撹拌
して放置した。9分後95℃、15分後粉状になった。
処理前三塩化PCB100%が処理後環境庁告示第13
号ハでN.Dであった。
Example 8 The treating agent shown in Table 3 was mixed with 30 g of liquid PCB prepared by using 62% CaO, 8% sodium silicate, and 30% slag, and 90 g of the treating agent was added and mixed, and 34 g of copper sulfate solution was added and left to stir. After 9 minutes, the mixture became 95 ° C., and after 15 minutes, it became powdery.
Before treatment, 100% of trichlorinated PCB is after treatment.
No. It was D.

【0014】[0014]

【実施例9】表3の処理剤を生石灰62%、珪酸ソーダ
ー8%、鉱滓30%で調合した。液体PCB25に処理
剤50gを入れて混合した後廃液(硫酸銅液)を25g
入れて3分間撹拌し放置した。1日養生した後、処理前
コンデンサー内に入った三塩化PCB100%が処理後
0.02ppmになった。固体状粒子を更に約160℃
に加熱した液体アスファルトを22g入れて加熱しなが
ら温度120℃〜160℃で5分撹拌した後、加熱せず
更に5分撹拌して被覆固定することにより処理前コンデ
ンサー内に入った三塩化PCB100%が不検出になっ
た。
Example 9 The treating agents shown in Table 3 were blended with 62% quicklime, 8% sodium silicate and 30% slag. After adding 50g of treatment agent to liquid PCB25 and mixing, 25g of waste liquid (copper sulfate solution)
The mixture was added, stirred for 3 minutes and left to stand. After curing for 1 day, 100% of trichloride PCB in the condenser before treatment became 0.02 ppm after treatment. Solid particles are further heated to about 160 ° C
After adding 22 g of heated liquid asphalt and stirring at a temperature of 120 ° C. to 160 ° C. for 5 minutes while heating, the mixture is further stirred for 5 minutes without heating to fix the coating, and 100% of trichloride PCB contained in the condenser before treatment. Was not detected.

【0015】[0015]

【実施例10】表2の処理剤をCaO50%鉱滓50%
で調合した。液体PCB25gに処理剤50gを入れ4
分間撹拌した後廃液(水銀59ppmを含む塩酸水)2
5gを入れて撹拌した後放置した。放置後7分で81℃
であった。2時間後約160℃に熱した液体アスファル
トを20g入れ加熱しながら温度120℃〜160℃で
約10分間撹拌して被覆固定した。処理前コンデンサー
内に入った三塩化PCB100%、水銀59ppmは処
理後不検出であった。
Example 10 The treating agent shown in Table 2 was treated with 50% CaO and 50% slag.
It was prepared in. Put 50g of treating agent in 25g of liquid PCB 4
Waste liquid (hydrochloric acid water containing 59 ppm of mercury) after stirring for 2 minutes 2
5 g was added, and the mixture was stirred and allowed to stand. 81 ° C in 7 minutes after leaving
Met. After 2 hours, 20 g of liquid asphalt heated to about 160 ° C. was charged, and the mixture was heated and stirred at a temperature of 120 ° C. to 160 ° C. for about 10 minutes to fix the coating. PCB 100% trichloride and mercury 59 ppm which entered the condenser before treatment were not detected after treatment.

【0016】[0016]

【実施例11】表2の処理剤をCaO40%鉱滓60%
調合した液体PCB25gに処理剤50gを入れ3分間
撹拌した後廃液(塩酸水)22gを入れて撹拌した後放
置した。放置後8分で84℃であった。1時間養生後1
00℃に加熱し、160℃に熱した液体アスファルトを
25g入れ温度120℃〜160℃で約10分間撹拌し
て被覆固定した。処理前コンデンサー内に入った三塩化
PCB100%、水銀59ppmは処理後不検出であっ
た。
[Example 11] CaO 40%, slag 60%
50 g of the treating agent was added to 25 g of the prepared liquid PCB, and the mixture was stirred for 3 minutes. Then, 22 g of a waste liquid (hydrochloric acid water) was added and the mixture was stirred and allowed to stand. The temperature was 84 ° C. 8 minutes after standing. 1 hour after curing 1
25 g of liquid asphalt heated to 00 ° C. and heated to 160 ° C. was put therein, and stirred at a temperature of 120 ° C. to 160 ° C. for about 10 minutes to fix the coating. PCB 100% trichloride and mercury 59 ppm which entered the condenser before treatment were not detected after treatment.

【0017】[0017]

【発明の効果】以上の実施例の示すごとく有害産業廃棄
物を不検出又は溶出を最小限にしアスファルトで更に固
体状粒子を被覆固定することにより非常に安全性の高い
廃棄物にして処理することが出来る。
EFFECTS OF THE INVENTION As shown in the above examples, hazardous industrial waste is treated as a very safe waste by undetecting or minimizing elution and further coating and fixing solid particles with asphalt. Can be done.

【0018】 [0018]

【0019】[0019]

【表1】 [Table 1]

【0020】[0020]

【表2】 [Table 2]

【0021】[0021]

【表3】 [Table 3]

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】油分及び又は液体有機塩素化合物及び重金
属を含有する産業廃棄物に混合しておいた界面活性を有
し反応を遅らす脂肪酸、生石灰、珪酸塩、又は脂肪酸、
生石灰、鉱滓、及び脂肪酸、生石灰、珪酸塩、鉱滓から
なる各処理剤を同量もしくは同量以上添加して混練しそ
の後必要量の水を混入して反応させ、産業廃棄物中に含
有する油分又は液体有機塩素化合物及び重金属を固定す
る事を特徴とする産業廃棄物の処理方法。
1. A fatty acid, quicklime, silicate, or fatty acid having surface activity and slowing the reaction, which has been mixed with an industrial waste containing oil and / or liquid organic chlorine compound and heavy metal.
Oils contained in industrial waste by adding the same amount or more than each treatment agent consisting of quick lime, slag, fatty acid, quick lime, silicate, and slag and kneading them, and then mixing and reacting necessary amount of water. Alternatively, a method for treating industrial waste, which comprises fixing a liquid organic chlorine compound and a heavy metal.
【請求項2】油分又は液体有機塩素化合物及び重金属を
含有する産業廃棄物に脂肪酸、生石灰、珪酸塩、又は脂
肪酸、生石灰、鉱滓、及び脂肪酸、生石灰、珪酸塩、鉱
滓からなる各処理剤を入れて混合し、その後必要量の
水、又は廃液を混入して反応させ、前記産業廃棄物を個
体状組成物と化し、この固体状組成物をアスファルトで
被覆固定して無害化する事を特徴とする処理方法。
2. Fatty acid, quick lime, silicate or fatty acid, quick lime, slag, and each treating agent consisting of fatty acid, quick lime, silicate and slag are added to industrial waste containing oil or liquid organic chlorine compound and heavy metal. It is characterized in that the required amount of water or a waste liquid is mixed and then reacted to make the industrial waste into a solid composition, and the solid composition is coated and fixed with asphalt to make it harmless. Processing method.
【請求項3】生石灰に界面活性を有し反応を遅らす脂肪
酸と珪酸塩を混合した処理剤。
3. A treatment agent in which quick lime is mixed with a silicate and a fatty acid which has a surface activity and delays the reaction.
【請求項4】生石灰に界面活性を有し反応を遅らす脂肪
酸とアルミナ生石灰、シリカ、酸化マグネシウム等を有
する鉱滓微粉塵からなる処理剤。
4. A treatment agent comprising a slag fine dust containing a fatty acid which has a surface activity and slows the reaction of quick lime, and alumina quick lime, silica, magnesium oxide and the like.
【請求項5】生石灰に界面活性を有し反応を遅らす脂肪
酸と珪酸塩及びアルミナ、生石灰、シリカ、酸化マグネ
シウム等を含有する鉱滓微粉塵からなる処理剤。
5. A treatment agent comprising a slag fine dust containing a fatty acid which has a surface activity and delays the reaction in quick lime, and a silicate and alumina, quick lime, silica, magnesium oxide and the like.
【請求項6】 上記請求項3.4.5処理剤中に脂肪酸
を添加せずに生石灰に界面活性を有し反応を遅らす物質
でコーテイングしたことを特徴とする処理剤。
6. The treatment agent as set forth in claim 3.4.5, which is obtained by coating with a substance which has a surface active property in quick lime and delays the reaction without adding a fatty acid to the treatment agent.
JP5355252A 1993-12-27 1993-12-27 Method for treating industrial waste, and treating agent Pending JPH07185034A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5355252A JPH07185034A (en) 1993-12-27 1993-12-27 Method for treating industrial waste, and treating agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5355252A JPH07185034A (en) 1993-12-27 1993-12-27 Method for treating industrial waste, and treating agent

Publications (1)

Publication Number Publication Date
JPH07185034A true JPH07185034A (en) 1995-07-25

Family

ID=18442860

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5355252A Pending JPH07185034A (en) 1993-12-27 1993-12-27 Method for treating industrial waste, and treating agent

Country Status (1)

Country Link
JP (1) JPH07185034A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002336373A (en) * 2001-05-17 2002-11-26 Miura Co Ltd Method of treating organic solution containing halogen organic compound
KR100397236B1 (en) * 2000-11-16 2003-09-19 한라산업개발 주식회사 Remediation method of contaminated subsurface and chlorinated organic compounds of ground water using hrm sludge or e/p dust
WO2005039702A1 (en) * 2003-10-28 2005-05-06 Nanyang Technological University A method and composition for stabilizing waste mercury compounds using ladle furnace slag

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100397236B1 (en) * 2000-11-16 2003-09-19 한라산업개발 주식회사 Remediation method of contaminated subsurface and chlorinated organic compounds of ground water using hrm sludge or e/p dust
JP2002336373A (en) * 2001-05-17 2002-11-26 Miura Co Ltd Method of treating organic solution containing halogen organic compound
WO2005039702A1 (en) * 2003-10-28 2005-05-06 Nanyang Technological University A method and composition for stabilizing waste mercury compounds using ladle furnace slag

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