JP2008231388A - Detoxifying treatment agent for hexavalent chromium-containing specific waste - Google Patents
Detoxifying treatment agent for hexavalent chromium-containing specific waste Download PDFInfo
- Publication number
- JP2008231388A JP2008231388A JP2007108707A JP2007108707A JP2008231388A JP 2008231388 A JP2008231388 A JP 2008231388A JP 2007108707 A JP2007108707 A JP 2007108707A JP 2007108707 A JP2007108707 A JP 2007108707A JP 2008231388 A JP2008231388 A JP 2008231388A
- Authority
- JP
- Japan
- Prior art keywords
- hexavalent chromium
- chromium
- wastes
- waste
- treatment agent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/78—Recycling of wood or furniture waste
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
本発明は、ステンレス鋼等の含クロム合金鋼やフェロクロム、金属クロム等の溶解、圧延、溶接、溶断等の加熱処理に伴って発生する含クロム鉱滓以外の、本発明が無害化処理の対象とする六価クロムを含有する特定廃棄物即ち、火葬場の骨灰、クロムをなめし材とする皮革なめし処理後の廃液及び皮革並びにその焼却灰、耐火クロム煉瓦などを焼く窯業廃棄物、クロムメッキ業界のメッキ廃液等廃棄物やその他六価クロムを含有する廃棄物、例えば、木造建築の廃材やその焼却灰、或いは某社の土壌埋め戻し剤、製品名フェロシルトに、六価クロムを含有した不要廃硫酸を意図的に混入して埋め戻し剤として販売し、埋め立てに使用して、その結果六価クロムが浸出流出して深刻な環境汚染を発生したが、このような汚染土壌埋め戻し剤等により汚染された廃棄物を特定しこれを処理対象とする無害化処理剤に係る。 The present invention is intended for the detoxification treatment of the present invention other than the chromium-containing iron ore that is generated by heat treatment such as melting, rolling, welding, fusing, etc. of chromium-containing alloy steel such as stainless steel, ferrochrome, and metal chromium. Specific waste containing hexavalent chromium, such as cremation skeleton bone ash, waste liquid and leather after leather tanning using chrome tanning materials, and incineration ash, refractory chrome bricks, etc. Waste such as plating waste and other waste containing hexavalent chromium, such as waste materials from wooden buildings and their incineration ash, or soil backfilling agent of the company, and product name ferrosilt, waste sulfuric acid containing hexavalent chromium Intentionally mixed and sold as a backfill, used as landfill, and as a result, hexavalent chromium leached out and caused serious environmental pollution. Identify the more contaminated waste according to detoxification treatment agent to be processed this.
上記のステンレス鋼等の含クロム合金鋼やフェロクロム、金属クロム等の溶解,圧延,溶接、溶断等の加熱処理に伴って発生する含クロム鉱滓の無害化処理については、本出願人の先願である発明の名称、含クロム鉱滓の処理方法(特許第3687014号)によって、極めて有効に無害化処理する方法を開発し、提案しているが、上記の如き特定廃棄物に関しては、従来有効な処理方法がなく、その極めて有害な廃棄物はそのまま放置され、危険な環境を作っていることが判明した。
上記の六価クロムの人体に対する危険性は、粘膜や皮膚を侵し、鼻中隔の穿孔や鼻、肺、咽喉などへの腫瘍の発生の恐れがある。
上記の特定廃棄物の一つである骨灰にも六価クロムが混入していることが、ジフェニルカルバジット法に準拠して発色させると、極めて明瞭に赤紫色の発色が認められることを発見した。これは火葬釜内の火格子がステンレス鋼製や含クロム鋼製であるため、火葬の際、釜は高温となり、火格子の鋼材のクロムが酸化されて鉱滓となり、脱落して骨灰に混入したものと推定される。
同じく、特定廃棄物に指定した、皮革のなめし工程でクロム錯塩の溶液をなめし剤として吸収させた際、その皮革の廃棄物に六価クロムが混入していることを上記検査法により確認した。
同様に、多様な耐火レンガの内、クロム鉄鉱を主原料とする耐火レンガは焼成の際、高温に曝されたクロム質が酸化して六価クロムが生成するものと推定され、上記検査法によりその存在を確認した。
更に、クロムメッキ法におけるメッキ浴には、クロム酸に少量の酸根を加えたものが使用されるが、電解に伴ってクロム量の一部が六価クロムに変性して廃液中に存在していることを上記検査法により確認した。
更に、木造建築物の廃材に塗布されていたと思われる薬種は定かではないが防腐剤や白蟻駆除剤の影響か、その廃材やその焼却灰から六価クロムの存在が同検査法により確認された。
これら六価クロムの還元により無害な三価クロムに変性させる手段として、従来は硫酸第一鉄か亜硫酸ソーダを還元剤として使用し、六価クロムを三価クロムに還元処理し、更に消石灰などのアルカリ剤を添加することにより水酸化クロムとして沈殿させ、これを分離除去する方法が採用されているが、斯かる処理方法は極めて煩雑で面倒なうえ、これらの還元剤は化学反応が穏やかなために、処理に長時間を必要とする欠点があり、且つ硫酸第一鉄の場合は多量の鉄イオンがやがては水酸化第二鉄として沈殿副生する欠点があり、また亜硫酸ソーダの場合は、その取扱いに際して亜硫酸ガスを発生するため、人体に対し有害であるなどの欠点があった。
これらの欠点を理由として、上記従来の処理法が普及せず、止むなく、無視放置されているのが実状である。Regarding the detoxification treatment of chromium-containing iron ore generated by heat treatment such as melting, rolling, welding, fusing, etc. of chromium-containing alloy steels such as stainless steel, ferrochrome, and metal chromium, the prior application of the present applicant. The name of a certain invention, a treatment method for chromium-containing iron ore (Patent No. 3687014), has been developed and proposed a method of detoxifying extremely effectively. It turned out that there was no method and the extremely hazardous waste was left as it was, creating a dangerous environment.
The above-mentioned danger of hexavalent chromium to the human body may affect the mucous membranes and skin, and may cause perforation of the nasal septum and tumors in the nose, lungs, throat, etc.
He discovered that bone ash, one of the above specified wastes, also contains hexavalent chromium, and when colored in accordance with the diphenylcarbazite method, the color of reddish purple is clearly recognized. . This is because the grate inside the cremation pot is made of stainless steel or chrome steel, and during the cremation, the kettle becomes hot, the chromium of the grate steel is oxidized and turned into slag, dropped off and mixed into bone ash Estimated.
Similarly, when the chromium complex salt solution was absorbed as a tanning agent in the leather tanning process designated as specific waste, it was confirmed by the above inspection method that hexavalent chromium was mixed in the leather waste.
Similarly, among the various refractory bricks, refractory bricks mainly made of chromite are estimated to oxidize the chromic material exposed to high temperatures during firing and produce hexavalent chromium. Its existence was confirmed.
Furthermore, the plating bath in the chromium plating method uses a chromic acid with a small amount of acid radicals, but part of the chromium content is transformed into hexavalent chromium due to electrolysis and is present in the waste liquid. It was confirmed by the above inspection method.
In addition, the type of chemical that seems to have been applied to the waste materials of wooden buildings is not clear, but the presence of hexavalent chromium was confirmed from the waste materials and their incinerated ash by the same inspection method. .
As a means of modifying these hexavalent chromium to harmless trivalent chromium, conventionally, ferrous sulfate or sodium sulfite was used as a reducing agent, hexavalent chromium was reduced to trivalent chromium, and further slaked lime, etc. A method is employed in which chromium hydroxide is precipitated by adding an alkali agent, and this is separated and removed. However, such a treatment method is extremely complicated and troublesome, and these reducing agents have a mild chemical reaction. In addition, there are drawbacks that require a long time for processing, and in the case of ferrous sulfate, there is a disadvantage that a large amount of iron ions eventually precipitate as ferric hydroxide, and in the case of sodium sulfite, Since the sulfurous acid gas is generated during the handling, there is a disadvantage that it is harmful to the human body.
Because of these drawbacks, the above-described conventional processing method is not widespread, and is unavoidably ignored.
叙上の実態に対し、本発明は上記特定した廃棄物中の六価クロムを従来にない簡単な方法で迅速に無害な三価クロムに還元可能な無害化処理剤を提供するにある。 In contrast to the above situation, the present invention is to provide a detoxifying agent capable of rapidly reducing hexavalent chromium in the specified waste to harmless trivalent chromium by an unprecedented simple method.
叙上の課題に鑑み、これを解決するための手段として次のごとく提案する。即ちアスコルビン酸及びその異性体若しくはそれらのナトリウム塩、カリウム塩、アンモニウム塩の一種又は二種以上を主成分とする溶液より成る、六価クロムを含有する特定廃棄物の無害化処理剤を解決の骨子とする。 In view of the above problems, the following are proposed as means for solving this problem. That is, a solution for detoxification of specified waste containing hexavalent chromium comprising a solution mainly composed of one or more of ascorbic acid and its isomers or sodium salts, potassium salts and ammonium salts thereof. The main point.
アスコルビン酸及びその異性体若しくはそれらのナトリウム塩、カリウム塩、アンモニウム塩等の誘導体の単体又は二種以上を含む溶液より成る本無害化処理剤を、本発明において特定した各廃棄物に散布するか浸漬する等の手段により、アスコルビン酸及びその誘導体の強力な且つ速効的な還元力によって当該各廃棄物に含まれている六価クロムを無害な三価クロムに還元する作用を奏するものである。尚、上記の溶液に対し、pH変化によって変色するpH指示薬を添加配合することにより、当該廃棄物に含有の六価クロムのアルカリ性に対しアスコルビン酸は酸性のため当該溶液の使用時にその色調の変化から、当該溶液の使用量の適量を決定する上で極めて有効である。
尚、当該溶液の溶媒は水が好適であるが、これに限定するものではなく、アルコール等他の溶媒の採用を妨げるものではなく、また溶液の浸透を助けるために界面活性剤を,湿潤性を付与するためにグリセリンなどを配合すれば更に効果的である。
尚又、アスコルビン酸水溶液の濃度について、その有効度を調査したところ、0.1重量%以下では還元効果はそれなりに有るものの、使用量が多くなり実用性に難点があるが、0.5重量%以上からは適度な使用量で顕著な還元効果が認められ、更にそれ以上の高濃度の場合は、より少量の使用量で足りるなど、処理すべき廃棄物の処理量や、含有する六価クロム量に応じて適宜選択すればよい。Whether to disperse this detoxifying agent consisting of a solution containing ascorbic acid and its isomers or derivatives thereof such as sodium salt, potassium salt, ammonium salt, etc., alone or in combination to each waste specified in the present invention. It has the effect of reducing the hexavalent chromium contained in each waste to harmless trivalent chromium by the powerful and fast reducing power of ascorbic acid and its derivatives by means such as immersion. In addition, ascorbic acid is acidic with respect to the alkalinity of hexavalent chromium contained in the waste by adding and blending a pH indicator that changes color due to a change in pH into the above solution, the color tone changes when the solution is used. Therefore, it is extremely effective in determining an appropriate amount of the solution to be used.
The solvent of the solution is preferably water, but is not limited to this. It does not prevent the use of other solvents such as alcohol, and a surfactant is used to help the solution to penetrate. It is more effective if glycerin or the like is blended in order to impart the.
In addition, when the concentration of the ascorbic acid aqueous solution was examined for its effectiveness, the reduction effect was moderate at 0.1% by weight or less, but the amount used was large and there was a problem in practicality, but 0.5% by weight. % Or more, a remarkable reduction effect is recognized at moderate usage, and if the concentration is higher than that, the amount of waste to be treated and the hexavalent content to be treated, such as a smaller amount, is sufficient. What is necessary is just to select suitably according to the amount of chromium.
本発明の処理対象とする特定廃棄物の一つである骨灰の少量を採取して、これに0.25%のジフェニルカルバジットのアセトン溶液を滴下したところ、赤紫色の発色が明瞭に認められ、明らかに六価クロムの存在が確認された。
そこで、同一の骨灰に対し、アスコルビン酸の5重量%水溶液を散布し、数分放置した後、上記アセトン溶液を滴下したところ、赤紫色の発色は全く認められず、六価クロムの存在は完全に消滅し、無害な三価のクロムに還元されたものと推定された。When a small amount of bone ash, which is one of the specific wastes to be treated according to the present invention, was collected and a 0.25% diphenylcarbaditone acetone solution was added dropwise thereto, a reddish purple color was clearly observed. Obviously, the presence of hexavalent chromium was confirmed.
Therefore, a 5% by weight aqueous solution of ascorbic acid was sprayed on the same bone ash, and after standing for several minutes, when the acetone solution was dropped, no reddish purple color was observed, and the presence of hexavalent chromium was complete. It was estimated that it was reduced to harmless trivalent chromium.
皮革のなめし剤として多用されるものに、クロム錯塩の溶液をなめし剤としているが、このなめし剤を使用してなめした皮革、焼却灰、及びその廃液に上記六価クロムの検知薬のアセトン溶液を滴下したところ、明瞭に赤紫色の発色が認められ、明らかに六価クロムの存在が確認できた。
そこで、同一の皮革及びその廃液に、上記実施例1と同様にアスコルビン酸の5重量%水溶液を散布し、数分放置した後、上記アセトン溶液を滴下したところ、赤紫色の発色は全然認められず、六価クロムの不存在を確認した。Chromium complex solution is used as a tanning agent in many tanning agents for leather, but leather tanned using this tanning agent, incineration ash, and acetone solution of the above hexavalent chromium detection agent in its waste liquid As a result, reddish purple color was clearly observed, and the presence of hexavalent chromium was clearly confirmed.
Therefore, as in Example 1, the same leather and its waste liquid were sprayed with a 5% by weight aqueous solution of ascorbic acid and allowed to stand for several minutes, and then the acetone solution was dropped. First, the absence of hexavalent chromium was confirmed.
クロム鉄鉱を主原料とする耐火煉瓦、通称クロム煉瓦を粉砕して、その粉末に上記の六価クロム検知薬たるアセトン溶液を滴下したところ、赤紫色の発色を確認した。明らかに六価クロムの存在が確認できた。
そこで、実施例1,2と同様、同濃度のアスコルビン酸の水溶液を散布後しばらく放置して、上記アセトン溶液を滴下したところ、六価クロムの存在を示す赤紫色の発色は全く認められなかった。即ち、六価クロムは三価のクロムに還元された。When refractory bricks, commonly called chromium bricks, containing chromite ore as the main raw material were pulverized and the acetone solution as the hexavalent chromium detector was dropped onto the powder, reddish purple color was confirmed. Obviously, the presence of hexavalent chromium was confirmed.
Therefore, as in Examples 1 and 2, after spraying an aqueous solution of ascorbic acid having the same concentration, the mixture was allowed to stand for a while and the acetone solution was dropped, and no reddish purple color indicating the presence of hexavalent chromium was observed. . That is, hexavalent chromium was reduced to trivalent chromium.
被メッキ材を陰極に、陽極材に鉛板を使用し、メッキ浴として、クロム酸に少量の酸根を加えて直流による電気分解処理を行って、被メッキ材にクロムメッキ処理を施した後、当該メッキ処理材の水洗後の排水を採取して、上記組成より成る六価クロムの検知薬であるアセトン溶液を滴下したところ、赤紫色の発色を見た。この現象から、当該メッキ処理後の排水中には明らかに六価クロムの存在が確認できた。
そこで、上記実施例と同様濃度のアスコルビン酸の水溶液を滴下して攪拌し、しばらく放置後、上記アセトン溶液を滴下して反応を観察したところ、なんら変化は無く、勿論赤紫色の発色は認められず、六価クロムの存在は全く確認できなかった。After using the lead to be plated as the cathode and the lead plate as the anode, and adding a small amount of acid radicals to the chromic acid as the plating bath, and subjecting the material to be plated to chrome plating, The waste water after the plating treatment was washed was collected and an acetone solution, which is a hexavalent chromium detection agent having the above composition, was dropped, and a reddish purple color was observed. From this phenomenon, the presence of hexavalent chromium was clearly confirmed in the waste water after the plating treatment.
Therefore, when an aqueous solution of ascorbic acid having the same concentration as in the above examples was dropped and stirred, and after standing for a while, the acetone solution was dropped and the reaction was observed. The presence of hexavalent chromium could not be confirmed at all.
最近、木造建築の廃材を採取し、念のため、六価クロムの存否を上記同様の検査手段により、分析したところ、中に六価クロムの存在を示す発色反応が出たものがあった。
そこで、当該被検体に、上記実施例に示したと同じ濃度のアスコルビン酸を散布して、しばらく放置後、上記アセトン溶液を滴下して発色反応をの有無を観察したが、全く発色反応は認められず、六価クロムの存在は認められなかった。当該廃材の焼却灰についても同様な結果を得ている。Recently, waste materials from wooden buildings were collected, and as a precaution, the presence or absence of hexavalent chromium was analyzed by the same inspection means as described above. As a result, there was a color reaction indicating the presence of hexavalent chromium.
Therefore, ascorbic acid having the same concentration as that shown in the above example was sprayed on the subject, and after standing for a while, the acetone solution was dropped to observe the presence or absence of a color reaction, but no color reaction was observed. In addition, the presence of hexavalent chromium was not observed. Similar results have been obtained for the incineration ash of the waste.
六価クロムの流出で深刻な環境汚染問題を発生した土壌埋め戻し材、製品名フェロシルトは、酸化チタンの製造過程で発生する廃硫酸から製造されるものであるが、六価クロムを含有すると推定される不要廃酸液を無害化処理することなく、当該製品に混入して起こした事件であるが、その原因はフェロシルト自体にはなく、問題は、不当に混入した不要廃硫酸液にある。この廃硫酸液中には既に六価クロムが存在していることが判明しているので、その無害化処理は本発明の処理剤の採用で完遂出来ることは敢えて実験するまでもなく推量できるものである。
また、これに類する六価クロム含有の産業廃棄物の無害化処理についても、本発明の無害化処理剤の適用によって処理可能なることは説明するまでもないと思料する。Ferrosilt, a soil backfill material that has caused serious environmental pollution problems due to the outflow of hexavalent chromium, is manufactured from waste sulfuric acid generated during the manufacturing process of titanium oxide, but is estimated to contain hexavalent chromium. This is an incident caused by mixing the unnecessary waste acid solution into the product without detoxifying it, but the cause is not in the ferrosilt itself, and the problem lies in the unnecessary waste sulfuric acid solution mixed in illegally. Since it has been found that hexavalent chromium is already present in this waste sulfuric acid solution, it can be estimated without deliberate experimentation that the detoxification treatment can be accomplished by employing the treatment agent of the present invention. It is.
In addition, it is considered that it is needless to say that the detoxification treatment of industrial waste containing hexavalent chromium similar to this can be treated by applying the detoxification treatment agent of the present invention.
前記実施例におけるアスコルビン酸に代えて、エリソルビン酸若しくはアスコルビン酸又はエリソルビン酸のナトリウム塩、カリウム塩、アンモニウム塩などの各誘導体を単体若しくは二種以上を用いて同様手法により各特定廃棄物の六価クロムの還元効果を試験したところ、同量のアスコルビン酸よりも若干その還元効果において劣るものの、濃度を適宜高めることにより、略同様な還元効果が得られることを確認した。 Instead of ascorbic acid in the above examples, erythorbic acid or ascorbic acid, or each derivative of sodium salt, potassium salt, ammonium salt, etc. of erythorbic acid is used alone or in combination of two or more by the same method. When the reduction effect of chromium was tested, it was confirmed that substantially the same reduction effect could be obtained by appropriately increasing the concentration, although the reduction effect was slightly inferior to that of the same amount of ascorbic acid.
本発明の六価クロム無害化処理剤によれば、本発明で特定した六価クロムを含有する廃棄物に対して、人体に健康を阻害する恐れなく安心して容易且つ迅速に無害化することを可能にしたものであり、六価クロムの存在に起因する深刻な環境汚染を防止する上で産業上極めて有益である。 According to the hexavalent chromium detoxifying treatment agent of the present invention, it is possible to easily and quickly detoxify the waste containing the hexavalent chromium specified in the present invention safely and without fear of hindering human health. It has been made possible, and is extremely useful in the industry for preventing serious environmental pollution caused by the presence of hexavalent chromium.
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2007108707A JP2008231388A (en) | 2007-03-20 | 2007-03-20 | Detoxifying treatment agent for hexavalent chromium-containing specific waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2007108707A JP2008231388A (en) | 2007-03-20 | 2007-03-20 | Detoxifying treatment agent for hexavalent chromium-containing specific waste |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2008231388A true JP2008231388A (en) | 2008-10-02 |
Family
ID=39904577
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2007108707A Pending JP2008231388A (en) | 2007-03-20 | 2007-03-20 | Detoxifying treatment agent for hexavalent chromium-containing specific waste |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2008231388A (en) |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2010082539A (en) * | 2008-09-30 | 2010-04-15 | Kurita Water Ind Ltd | Method of treating soil or slag |
JP2011024439A (en) * | 2009-07-22 | 2011-02-10 | Tokyo Metropolitan Government | Method for preparing sample nucleic acid |
WO2014024828A1 (en) * | 2012-08-08 | 2014-02-13 | 株式会社金子コンクリート | Construction filler |
JP2014034681A (en) * | 2013-06-25 | 2014-02-24 | Kaneko Concrete:Kk | Filler for construction |
JP2014189594A (en) * | 2013-03-26 | 2014-10-06 | Hiroo Ninagawa | Hexavalent chromium reducing agent and fixing agent, and hexavalent chromium treatment method using the agents |
EP3098208A1 (en) * | 2015-05-28 | 2016-11-30 | Refractory Intellectual Property GmbH & Co. KG | Method for producing a raw material for the formation of fire-proof ceramic products, raw material produced from same and a raw material for the production of fire-proof ceramic products |
KR20170033384A (en) | 2014-08-04 | 2017-03-24 | 시티즌 도케이 가부시키가이샤 | Leather or leather article and method for producing same, hexavalent chromium treatment agent, method for treating hexavalent chromium in crude leather or curde leather article |
JP2017132952A (en) * | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Manufacturing method of leather or leather product using hexavalent chromium treatment agent and leather or leather product using hexavalent chromium treatment agent |
WO2017131138A1 (en) * | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Inspection liquid for inspecting whether leather has been treated using hexavalent chromium reducing compound |
WO2017131139A1 (en) | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Hexavalent chromium treatment agent, and leather or leather product using same |
WO2018163621A1 (en) * | 2017-03-10 | 2018-09-13 | シチズン時計株式会社 | Powdery composition for hexavalent chromium treatment, tablet, and method for producing leather |
WO2019067972A1 (en) * | 2017-09-28 | 2019-04-04 | Hach Company | In-situ reduction of hexavalent chromium |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH09248543A (en) * | 1996-03-13 | 1997-09-22 | Chem Yamamoto:Kk | Treatment of chromium containing slag |
JPH11104611A (en) * | 1997-06-26 | 1999-04-20 | Chem Land Holdings Inc | Method for reducing hexavalent chromium contained in soil, cumulus deposit, industrial waste and other contaminated material by using ascorbic acid |
JPH11267602A (en) * | 1998-03-25 | 1999-10-05 | Mitsubishi Heavy Ind Ltd | Treatment of collected ash from coal combustion waste gas |
JP2001311140A (en) * | 2000-05-01 | 2001-11-09 | Chem Grouting Co Ltd | Hazardous material treatment method |
-
2007
- 2007-03-20 JP JP2007108707A patent/JP2008231388A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH09248543A (en) * | 1996-03-13 | 1997-09-22 | Chem Yamamoto:Kk | Treatment of chromium containing slag |
JPH11104611A (en) * | 1997-06-26 | 1999-04-20 | Chem Land Holdings Inc | Method for reducing hexavalent chromium contained in soil, cumulus deposit, industrial waste and other contaminated material by using ascorbic acid |
JPH11267602A (en) * | 1998-03-25 | 1999-10-05 | Mitsubishi Heavy Ind Ltd | Treatment of collected ash from coal combustion waste gas |
JP2001311140A (en) * | 2000-05-01 | 2001-11-09 | Chem Grouting Co Ltd | Hazardous material treatment method |
Cited By (23)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2010082539A (en) * | 2008-09-30 | 2010-04-15 | Kurita Water Ind Ltd | Method of treating soil or slag |
JP2011024439A (en) * | 2009-07-22 | 2011-02-10 | Tokyo Metropolitan Government | Method for preparing sample nucleic acid |
WO2014024828A1 (en) * | 2012-08-08 | 2014-02-13 | 株式会社金子コンクリート | Construction filler |
JP2014189594A (en) * | 2013-03-26 | 2014-10-06 | Hiroo Ninagawa | Hexavalent chromium reducing agent and fixing agent, and hexavalent chromium treatment method using the agents |
JP2014034681A (en) * | 2013-06-25 | 2014-02-24 | Kaneko Concrete:Kk | Filler for construction |
CN106661638A (en) * | 2014-08-04 | 2017-05-10 | 西铁城时计株式会社 | Leather or leather article and method for producing same, hexavalent chromium treatment agent, method for treating hexavalent chromium in crude leather or crude leather article |
US10358686B2 (en) | 2014-08-04 | 2019-07-23 | Citizen Watch Co., Ltd. | Leather or leather article and method for producing same, hexavalent chromium treatment agent, method for treating hexavalent chromium in crude leather or crude leather article |
KR20170033384A (en) | 2014-08-04 | 2017-03-24 | 시티즌 도케이 가부시키가이샤 | Leather or leather article and method for producing same, hexavalent chromium treatment agent, method for treating hexavalent chromium in crude leather or curde leather article |
US10233122B2 (en) | 2015-05-28 | 2019-03-19 | Refractory Intellectual Property Gmbh & Co. Kg | Method for producing a raw material for the production of refractory ceramic products, a raw material produced according to the method and a raw material for producing refractory ceramic products |
EP3098208A1 (en) * | 2015-05-28 | 2016-11-30 | Refractory Intellectual Property GmbH & Co. KG | Method for producing a raw material for the formation of fire-proof ceramic products, raw material produced from same and a raw material for the production of fire-proof ceramic products |
WO2016188648A1 (en) * | 2015-05-28 | 2016-12-01 | Refractory Intellectual Property Gmbh & Co. Kg | Method for producing a raw material for the production of refractory ceramic products, a raw material produced according to the method and a raw material for producing refractory ceramic products |
WO2017131138A1 (en) * | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Inspection liquid for inspecting whether leather has been treated using hexavalent chromium reducing compound |
WO2017131139A1 (en) | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Hexavalent chromium treatment agent, and leather or leather product using same |
JP2017132952A (en) * | 2016-01-29 | 2017-08-03 | シチズン時計株式会社 | Manufacturing method of leather or leather product using hexavalent chromium treatment agent and leather or leather product using hexavalent chromium treatment agent |
JPWO2017131139A1 (en) * | 2016-01-29 | 2018-11-29 | シチズン時計株式会社 | Hexavalent chromium treatment agent and leather or leather product using the same |
US20190024197A1 (en) * | 2016-01-29 | 2019-01-24 | Citizen Watch Co., Ltd. | Hexavalent chromium treatment agent and leather or leather article produced using the same |
US10648048B2 (en) | 2016-01-29 | 2020-05-12 | Citizen Watch Co., Ltd. | Hexavalent chromium treatment agent and leather or leather article produced using the same |
WO2018163621A1 (en) * | 2017-03-10 | 2018-09-13 | シチズン時計株式会社 | Powdery composition for hexavalent chromium treatment, tablet, and method for producing leather |
CN110268031A (en) * | 2017-03-10 | 2019-09-20 | 西铁城时计株式会社 | The manufacturing method of the powdered compositions of 6 valence chromium processing, tablet and leather |
JPWO2018163621A1 (en) * | 2017-03-10 | 2020-01-09 | シチズン時計株式会社 | Powdery composition for treating hexavalent chromium, tablet and method for producing leather |
CN110268031B (en) * | 2017-03-10 | 2022-07-08 | 西铁城时计株式会社 | Powdery composition for 6-valent chromium treatment, tablet, and method for producing leather |
CN111051250A (en) * | 2017-09-28 | 2020-04-21 | 哈希公司 | In situ reduction and quenching of hexavalent chromium |
WO2019067972A1 (en) * | 2017-09-28 | 2019-04-04 | Hach Company | In-situ reduction of hexavalent chromium |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP2008231388A (en) | Detoxifying treatment agent for hexavalent chromium-containing specific waste | |
CA1331824C (en) | Compositions to encapsulate chromium, arsenic, and other toxic metals in wastes | |
JP5176839B2 (en) | Soil or slag treatment method | |
JP2014054602A (en) | Insolubilizer of harmful matter and insolubilization treatment method of harmful matter | |
JP2006289306A (en) | Method of suppressing elution of fluorine and heavy metal from waste and stabilizing agent | |
CN102718440A (en) | Modified blast furnace slag cement solidified body and method for treating chromium slag by using same | |
CN105570900B (en) | A kind of detoxification of chromium slag | |
JP3473444B2 (en) | Method for treating chromium oxide-containing material | |
JP2008238150A (en) | Detoxification agent for contaminated soil and industrial waste containing hexavalent chromium | |
JP3687014B2 (en) | Treatment method of chromium-containing iron ore | |
Sharaf et al. | Reduction of hexavalent chromium from chrome shavings | |
MXPA02004510A (en) | Treatment of electric arc furnace dust to resist acid and alkaline leaching of heavy metals. | |
CN107684688A (en) | A kind of high-temperature detoxification method of chromium slag | |
JP2649625B2 (en) | Electrolyte for electrolytic polishing of chromium-containing alloy steel | |
JP2003062541A (en) | Method for treating member having hexa-valent chromium | |
CN104893784A (en) | Processing method using cyanide-containing waste polymer as cement plant substitution fuel | |
JP3722047B2 (en) | Hexavalent chromium insolubilizing agent and hexavalent chromium insolubilizing method | |
JP3221564B2 (en) | Method for treating chromium oxide-containing material | |
JP5470699B2 (en) | Detoxification method for heavy metal-containing basic waste | |
JP6850500B1 (en) | Composite treatment agent and composite treatment method | |
Pei et al. | Optimization of Hexavalent Chromium Removal from Wastewater by Ferrite Precipitation. | |
JPH0219486A (en) | Film removing treatment of metal and alloy | |
JP2004025115A (en) | Method for insolubilizing heavy metal in treated material of organic halide-polluted body | |
JP3221565B2 (en) | Method for treating chromium oxide-containing substance, roadbed material, civil engineering landfill material, and temporary material using the same | |
JPS5561925A (en) | Scrubbing treatment of exhaust gas containing heavy metal |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20100312 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20120510 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20120522 |
|
A02 | Decision of refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A02 Effective date: 20130122 |