JP2009291730A5 - - Google Patents
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- JP2009291730A5 JP2009291730A5 JP2008148893A JP2008148893A JP2009291730A5 JP 2009291730 A5 JP2009291730 A5 JP 2009291730A5 JP 2008148893 A JP2008148893 A JP 2008148893A JP 2008148893 A JP2008148893 A JP 2008148893A JP 2009291730 A5 JP2009291730 A5 JP 2009291730A5
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Description
以下において、実施例15を含む本発明の複数の実施例、比較例および参考例を示すが、本発明は、これらの実施例等によって何等限定されるものではなく、特許請求の範囲によって特定されるものであることはいうまでもない。 In the following, a plurality of examples, comparative examples and reference examples of the present invention including Example 15 are shown, but the present invention is not limited in any way by these examples and is specified by the claims. Needless to say, it is something.
参考例A
アスベストヤーン0.5 gとオルト珪酸ナトリウムn水塩(SiO2/M2Oモル比=0.5)0.5 gとを容量50 mlの坩堝に入れ、薬匙で約10秒間かき混ぜた。その後、坩堝に蓋をして電気加熱炉(光洋リンドバーグ株式会社製電気炉KBF-894N)内に装入し、該電気炉内において900℃で1時間加熱した。その後、室温まで放冷し、内容物を取り出して走査電子顕微鏡により観察した。
Reference example A
0.5 g of asbestos yarn and 0.5 g of sodium orthosilicate n-hydrate (SiO 2 / M 2 O molar ratio = 0.5) were put in a crucible with a capacity of 50 ml, and the mixture was stirred for about 10 seconds with a medicine basket. Thereafter, the crucible was covered and charged in an electric heating furnace (Electric furnace KBF-894N manufactured by Koyo Lindberg Co., Ltd.), and heated in the electric furnace at 900 ° C. for 1 hour. Thereafter, the mixture was allowed to cool to room temperature, and the contents were taken out and observed with a scanning electron microscope.
参考例B
珪酸ナトリウムとして0.5 gの無水メタ珪酸ナトリウム(SiO2/M2Oモル比=1)を使用すること以外、参考例Aと同様の操作を行った。
Reference example B
The same operation as in Reference Example A was performed, except that 0.5 g of anhydrous sodium metasilicate (SiO 2 / M 2 O molar ratio = 1) was used as the sodium silicate.
参考例C
珪酸ナトリウムとして0.5 gのエコレイヤ粉末(SiO2/M2Oモル比=2)を使用すること以外、参考例Aと同様の操作を行った。
Reference example C
The same operation as in Reference Example A was performed, except that 0.5 g of Ecolayer powder (SiO 2 / M 2 O molar ratio = 2) was used as sodium silicate.
参考例D
珪酸ナトリウムとして0.5 gの中モルカレット(SiO2/M2Oモル比=3)を使用すること以外、参考例Aと同様の操作を行った。
Reference example D
The same operation as in Reference Example A was performed, except that 0.5 g of medium mole cullet (SiO 2 / M 2 O molar ratio = 3) was used as sodium silicate.
参考例EおよびF
900℃で加熱する代わりに750℃(参考例E)または1200℃(参考例F)で加熱すること以外、参考例Aと同様の操作を行った(なお、1200℃で加熱する場合には、電気加熱炉として株式会社モトヤマ製酸化雰囲気超高温電気炉KB-2030Dを使用した)。
Reference examples E and F
The same operation as in Reference Example A was performed except that heating was performed at 750 ° C. ( Reference Example E ) or 1200 ° C. ( Reference Example F ) instead of heating at 900 ° C. (In the case of heating at 1200 ° C., We used Motoyama Co., Ltd. oxidation atmosphere ultra-high temperature electric furnace KB-2030D as an electric heating furnace.
参考例G〜I
900℃で加熱する代わりに600℃(参考例G)、750℃(参考例H)または1200℃(参考例I)で加熱すること以外、参考例Bと同様の操作を行った(なお、1200℃で加熱する場合には、電気加熱炉として株式会社モトヤマ製酸化雰囲気超高温電気炉KB-2030Dを使用した)。
Reference examples GI
Instead of heating at 900 ° C., the same operation as in Reference Example B was carried out except that heating was carried out at 600 ° C. ( Reference Example G ), 750 ° C. ( Reference Example H ) or 1200 ° C. ( Reference Example I ). When heating at ℃, we used Motoyama Co., Ltd. oxidizing atmosphere ultra-high temperature electric furnace KB-2030D).
それぞれの電子顕微鏡(参考例GおよびH)または目視(参考例I)による観察結果は、下記の表2に示したとおりである。 The observation results of each electron microscope ( Reference Examples G and H ) or visual observation ( Reference Example I ) are as shown in Table 2 below.
参考例J〜M
900℃で加熱する代わりに600℃(参考例J)、750℃(参考例K)、1000℃(参考例L)または1200℃(参考例M)で加熱すること以外、参考例Cと同様の操作を行った(なお、1000℃および1200℃で加熱する場合には、電気加熱炉として株式会社モトヤマ製酸化雰囲気超高温電気炉KB-2030Dを使用した)。
Reference examples J-M
Similar to Reference Example C , except heating at 600 ° C. ( Reference Example J ), 750 ° C. ( Reference Example K ), 1000 ° C. ( Reference Example L ) or 1200 ° C. ( Reference Example M ) instead of heating at 900 ° C. The operation was performed (in the case of heating at 1000 ° C. and 1200 ° C., an ultrahigh temperature electric furnace KB-2030D manufactured by Motoyama Co., Ltd. was used as the electric heating furnace).
それぞれの電子顕微鏡(参考例J、KおよびL)または目視(参考例M)による観察結果は、下記の表2に示したとおりである。 The observation results of each electron microscope ( Reference Examples J, K and L 1 ) or visually ( Reference Example M 1 ) are as shown in Table 2 below.
参考例N
900℃で加熱する代わりに1200℃(参考例N)で加熱すること以外、参考例Dと同様の操作を行った(なお、電気加熱炉として株式会社モトヤマ製酸化雰囲気超高温電気炉KB-2030Dを使用した)。
Reference example N
The same operation as in Reference Example D was performed except that heating was performed at 1200 ° C. ( Reference Example N ) instead of heating at 900 ° C. It was used).
比較例1
参考例Aで使用したアスベストヤーン0.5 gを容量50 mlの坩堝に入れ、坩堝に蓋をして電気加熱炉(光洋リンドバーグ株式会社製電気炉KBF-894N)内に装入し、該電気炉内において900℃で1時間加熱した。その後、室温まで放冷し、坩堝内を目視によって観察した。その結果、坩堝内のアスベストヤーンは若干縮み、ごわついたような状態になっていた。この加熱処理後の坩堝内容物を取り出して走査電子顕微鏡により観察したところ、針状の繊維構造は失われていなかった(図4-B(c))。
Comparative Example 1
Place 0.5 g of asbestos yarn used in Reference Example A into a crucible with a capacity of 50 ml, cover the crucible and place it in an electric heating furnace (Electric furnace KBF-894N manufactured by Koyo Lindberg Co., Ltd.). At 900 ° C. for 1 hour. Thereafter, the mixture was allowed to cool to room temperature, and the inside of the crucible was visually observed. As a result, the asbestos yarn in the crucible was slightly shrunk and was in a stiff state. When the crucible contents after the heat treatment were taken out and observed with a scanning electron microscope, the needle-like fiber structure was not lost (FIG. 4-B (c)).
比較例2
珪酸ナトリウムとして、SiO2/M2Oのモル比が2である珪酸ナトリウムを30%含む水溶液1.66 gを使うこと以外、参考例Aと同様の操作を行った。坩堝を電気炉に装入して加熱したところ、急速に発泡し、坩堝から内容物があふれ出したため試験を中止した。
Comparative Example 2
The same operation as in Reference Example A was performed except that 1.66 g of an aqueous solution containing 30% sodium silicate having a SiO 2 / M 2 O molar ratio of 2 was used as sodium silicate. When the crucible was charged in an electric furnace and heated, foaming occurred rapidly and the contents overflowed from the crucible, so the test was stopped.
比較例3
珪酸ナトリウムとして0.5gの無水珪酸(SiO2/M2Oのモル比は無限大に相当)を使うこと以外、参考例Aと同様の操作を行った。比較例1と同様、坩堝内のアスベストヤーンは若干縮み、ごわついたような状態になっていた。この加熱処理後の石綿リボンを走査電子顕微鏡によって観察したところ、針状の繊維構造は失われていなかった。
Comparative Example 3
The same operation as in Reference Example A was performed, except that 0.5 g of anhydrous silicic acid (SiO 2 / M 2 O molar ratio was equivalent to infinity) was used as sodium silicate. As in Comparative Example 1, the asbestos yarn in the crucible was slightly shrunk and was in a stiff state. When the asbestos ribbon after the heat treatment was observed with a scanning electron microscope, the needle-like fiber structure was not lost.
珪酸ナトリウムとして0.5 gの粉末珪酸ナトリウムJIS-1号(水ガラスを乾燥させた粉末で20重量%の含水率を有する)を使用すること以外、参考例Aと同様の操作を行った。
The same operation as in Reference Example A was performed except that 0.5 g of powdered sodium silicate JIS-1 (powder obtained by drying water glass and having a water content of 20% by weight) was used as sodium silicate.
実施例16
珪酸ナトリウムとして0.5 gのメタ珪酸ナトリウム・9水塩(含水率57重量%)を使用すること以外、参考例Aと同様の操作を行った。
Example 16
The same operation as in Reference Example A was carried out except that 0.5 g of sodium metasilicate.9 hydrate (water content 57% by weight) was used as sodium silicate.
以下の表3に、異なる含水率を有する珪酸アルカリを用いて種々の温度で加熱処理を行った場合における加熱後の石綿の状態(電子顕微鏡または目視による観察結果)をまとめて記載した。なお、参考例C、K、Mについては既に表2に記載したものであるが、各含水率間での比較を容易にするために表3においても記載してある。 Table 3 below summarizes the state of asbestos after heating (electron microscope or observation results by visual observation) when heat treatment was performed at various temperatures using alkali silicates having different moisture contents. Reference examples C, K, and M have already been described in Table 2, but are also described in Table 3 to facilitate comparison between the respective moisture contents.
表3の結果からは、含水率が高くなる程、石綿繊維同士の融着が顕著になり、それに伴って石綿の構造喪失度が高くなる傾向が認められる。
From the results in Table 3, it can be seen that as the moisture content increases, the asbestos fibers are more likely to be fused with each other, and the degree of asbestos structure loss tends to increase accordingly.
参考例OおよびP
珪酸ナトリウムとして0.5gのエコレイヤ顆粒(平均粒子径700μm)(参考例O)またはエコレイヤ粗粒(平均粒子径3.4 mm)(参考例P)を使用すること以外、参考例Aと同様の操作を行った。
Reference examples O and P
Perform the same operation as in Reference Example A , except that 0.5 g of Ecolayer granules (average particle size 700 μm) ( Reference Example O ) or Ecolayer coarse particles (Average particle size 3.4 mm) ( Reference Example P ) are used as sodium silicate. It was.
以下の表4に、異なる平均粒子径を有する珪酸アルカリを用いて加熱処理を行った場合における加熱処理後の石綿の状態(電子顕微鏡による観察結果)をまとめて記載した。なお、参考例Cについては既に表2に記載したものであるが、各平均粒子径間での比較を容易にするために表4においても記載してある。 In Table 4 below, the states of asbestos after heat treatment (observation results by an electron microscope) when heat treatment is performed using alkali silicates having different average particle diameters are collectively described. Reference Example C is already described in Table 2, but is also described in Table 4 in order to facilitate comparison between the average particle diameters.
表4の結果からは、平均粒子径が低い程、加熱処理後の石綿の構造喪失度が高くなる傾向が認められる。
From the results in Table 4, it can be seen that the lower the average particle diameter, the higher the degree of structural loss of asbestos after heat treatment.
Claims (4)
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2008148893A JP2009291730A (en) | 2008-06-06 | 2008-06-06 | Method for detoxifying solid waste containing asbestos |
CN200980114075.XA CN102015135B (en) | 2008-06-06 | 2009-06-02 | Method of detoxifying asbestos-containing solid waste |
PCT/JP2009/002461 WO2009147834A1 (en) | 2008-06-06 | 2009-06-02 | Method of detoxifying asbestos-containing solid waste |
KR1020107022296A KR20110028251A (en) | 2008-06-06 | 2009-06-02 | Method of detoxifying asbestos-containing solid waste |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2008148893A JP2009291730A (en) | 2008-06-06 | 2008-06-06 | Method for detoxifying solid waste containing asbestos |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2009291730A JP2009291730A (en) | 2009-12-17 |
JP2009291730A5 true JP2009291730A5 (en) | 2011-04-07 |
Family
ID=41397917
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2008148893A Pending JP2009291730A (en) | 2008-06-06 | 2008-06-06 | Method for detoxifying solid waste containing asbestos |
Country Status (4)
Country | Link |
---|---|
JP (1) | JP2009291730A (en) |
KR (1) | KR20110028251A (en) |
CN (1) | CN102015135B (en) |
WO (1) | WO2009147834A1 (en) |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101240571B1 (en) * | 2011-04-13 | 2013-03-13 | 이종원 | Composition of Preventing Dust-Scattering and Method of Preventing Dust-Scattering Using the Same |
JP2014237069A (en) * | 2013-06-05 | 2014-12-18 | 独立行政法人産業技術総合研究所 | Detoxification method of waste containing asbestos |
PL422697A1 (en) * | 2017-08-30 | 2019-03-11 | Jerzy Dora | Method for rendering harmless asbestos and/or asbestos-containing materials |
KR102046866B1 (en) * | 2018-01-26 | 2019-11-20 | 주식회사 모노리스 | Method for decomposing asbestos-containing materials using ilmenite or carbon-based materials |
CN113843257B (en) * | 2021-09-22 | 2023-06-20 | 西南科技大学 | Harmless treatment method of asbestos waste, asbestos-free material and application thereof |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62237984A (en) * | 1986-04-08 | 1987-10-17 | Meisei Kogyo Kk | Waste materials treatment for asbestos-containing substance |
ATE118366T1 (en) * | 1989-06-29 | 1995-03-15 | Roger B Ek | MINERALOGICAL IMPLEMENTATION OF ASBESTOS WASTE. |
JP3908292B2 (en) * | 1995-10-13 | 2007-04-25 | 有限会社アドセラミックス研究所 | Method for producing asbestos material sintered body |
JPH10212146A (en) * | 1997-01-24 | 1998-08-11 | Akutoron Group Kk | Cement admixture and is application |
JP3928135B2 (en) * | 2005-11-08 | 2007-06-13 | 株式会社クレー・バーン技術研究所 | Dust-proof material and processing method for asbestos |
JP4758268B2 (en) * | 2006-04-03 | 2011-08-24 | 株式会社大和地質研究所 | On-site waste asbestos detoxification system |
JP4740200B2 (en) * | 2006-09-29 | 2011-08-03 | ニチアス株式会社 | Asbestos-containing material scattering prevention method, asbestos-containing material waste material treatment method, asbestos waste material melting treatment method, asbestos waste material treatment product and asbestos fusion treatment product |
-
2008
- 2008-06-06 JP JP2008148893A patent/JP2009291730A/en active Pending
-
2009
- 2009-06-02 WO PCT/JP2009/002461 patent/WO2009147834A1/en active Application Filing
- 2009-06-02 KR KR1020107022296A patent/KR20110028251A/en not_active Application Discontinuation
- 2009-06-02 CN CN200980114075.XA patent/CN102015135B/en not_active Expired - Fee Related
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