US20070270625A1 - Treatment of Polysilazane Waste - Google Patents

Treatment of Polysilazane Waste Download PDF

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Publication number
US20070270625A1
US20070270625A1 US11/419,009 US41900906A US2007270625A1 US 20070270625 A1 US20070270625 A1 US 20070270625A1 US 41900906 A US41900906 A US 41900906A US 2007270625 A1 US2007270625 A1 US 2007270625A1
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US
United States
Prior art keywords
waste
acid
treatment stabilizer
polysilazane
ether
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.)
Abandoned
Application number
US11/419,009
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English (en)
Inventor
Joshua Gurman
Joseph E. Oberlander
Bruce Kiker
Tom Carl
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.)
EMD Performance Materials Corp
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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 US11/419,009 priority Critical patent/US20070270625A1/en
Assigned to AZ ELECTRONIC MATERIALS USA CORP. reassignment AZ ELECTRONIC MATERIALS USA CORP. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: GURMAN, JOSHUA, OBERLANDER, JOSEPH E., KIKER, BRUCE, CARL, TOM
Priority to TW96116743A priority patent/TWI426095B/zh
Priority to JP2009510569A priority patent/JP5298337B2/ja
Priority to CNA2007800180426A priority patent/CN101448885A/zh
Priority to KR20087028567A priority patent/KR101402548B1/ko
Priority to DE200760003350 priority patent/DE602007003350D1/de
Priority to PCT/IB2007/001347 priority patent/WO2007135556A1/en
Priority to EP20070734653 priority patent/EP2024432B1/en
Publication of US20070270625A1 publication Critical patent/US20070270625A1/en
Priority to IL195004A priority patent/IL195004A0/en
Priority to MYPI20084652 priority patent/MY144317A/en
Abandoned legal-status Critical Current

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Classifications

    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00—Recovery or working-up of waste materials
    • C08J11/04—Recovery or working-up of waste materials of polymers
    • C08J11/06—Recovery or working-up of waste materials of polymers without chemical reactions
    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00—Recovery or working-up of waste materials
    • C08J11/04—Recovery or working-up of waste materials of polymers
    • C08J11/10—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/18—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material
    • C08J11/22—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material by treatment with organic oxygen-containing compounds
    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08G—MACROMOLECULAR COMPOUNDS OBTAINED OTHERWISE THAN BY REACTIONS ONLY INVOLVING UNSATURATED CARBON-TO-CARBON BONDS
    • C08G77/00—Macromolecular compounds obtained by reactions forming a linkage containing silicon with or without sulfur, nitrogen, oxygen or carbon in the main chain of the macromolecule
    • C08G77/04—Polysiloxanes
    • C08G77/32—Post-polymerisation treatment
    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00—Recovery or working-up of waste materials
    • C08J11/04—Recovery or working-up of waste materials of polymers
    • C08J11/10—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/18—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material
    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08K—Use of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K5/00—Use of organic ingredients
    • C08K5/04—Oxygen-containing compounds
    • C08K5/05—Alcohols; Metal alcoholates
    • C—CHEMISTRY; METALLURGY
    • C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2383/00—Characterised by the use of macromolecular compounds obtained by reactions forming in the main chain of the macromolecule a linkage containing silicon with or without sulfur, nitrogen, oxygen, or carbon only; Derivatives of such polymers
    • C08J2383/16—Characterised by the use of macromolecular compounds obtained by reactions forming in the main chain of the macromolecule a linkage containing silicon with or without sulfur, nitrogen, oxygen, or carbon only; Derivatives of such polymers in which all the silicon atoms are connected by linkages other than oxygen atoms
    • 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
    • Y02W30/62—Plastics recycling; Rubber recycling

Definitions

  • the present invention relates to a method of treating polysilazane waste material in order to facilitate a safer, more cost effective disposal of the waste.
  • Polysilazanes are used to produce solid silicate (i.e. glass) coatings on substrate surfaces, for example, semiconductor devices and flat panel screens.
  • an edge bead removal process using an edge bead remover solvent system, is performed.
  • all residual polysilazane is rinsed from the equipment surfaces using organic solutions.
  • the polysilazane-organic process waste streams are then rinsed down the drain, through a transfer line to a process waste holding container. After filling, the process waste holding container can be sealed or the liquid can be transferred to other waste containers to be transferred for waste disposal.
  • the current disposal process entails having the unstabilized polysilazane-organic process waste stream collected in a waste holding container until the container is full. Once the holding container is full, the waste is transferred to a vented drum for interim stabilization of the waste. Finally, the drum is sealed and sent for waste disposal.
  • Unstabilized polysilazane waste can react with unintentionally present contaminants (i.e. OH-donor chemicals; water, alcohols, aldehydes, etc.). The reaction causes a decomposition of the polysilazane to produce hydrogen, ammonia and silane gases.
  • the polysilazane-organic waste must be stabilized (also known as neutralized) so that if the waste solution comes into contact with any unintentional contaminants it will not undergo further decomposition.
  • the waste drums are left vented to allow for the polysilazane-organic waste to off-gas, with the recommended holding period being ten days. If this recommended vent time is insufficient for the polysilazane-organic waste to “stabilize” it will continue to off-gas. This further decomposition can result in deformation of the waste containers (i.e. bulging) which can ultimately lead to the complete catastrophic failure of the container. This poses a serious potential health and safety issue.
  • the present invention is related to a process for treating polysilazane waste comprising contacting the polysilazane waste with a treatment stabilizer selected from the group consisting of an OH-containing compound and an OH-containing compound and alkaline mixture.
  • the treatment stabilizer, or treatment stabilizer solution can contact the polysilazane waste by (a) injecting the treatment stabilizer into a waste stream of polysilazane waste; (b) adding the treatment stabilizer into a container containing polysilazane waste; or (c) adding the polysilazane waste into a container containing treatment stabilizer.
  • OH containing compound examples include, but are not limited to, for example, alcohols, ether alcohols, glycols, and carboxylic acids, and mixtures thereof.
  • alcohols include, but are not limited to, methanol, ethanol, n-propanol, isopropanol, n-butanol, sec-butanol, phenol, and the like.
  • ether alcohols include, but are not limited to, for example, 1-butoxyethoxy-2-propanol, 3-methyl-3-methoxybutanol, ethylene glycol n-butyl ether, ethylene glycol phenyl ether, ethylene glycol propyl ether, diethylene glycol hexyl ether, diethylene glycol monoethyl ether, diethylene glycol monomethyl ether, diethylene glycol monobutyl ether, diethylene glycol monopropyl ether, propylene glycol ethyl ether, propylene glycol isobutyl ether, propylene glycol monomethyl ether, propylene glycol monobutyl ether, propylene glycol monoethyl ether, propylene glycol n-propyl ether, propylene glycol phenyl ether, propylene glycol-t-butyl ether, dipropylene glycol ethyl ether, dipropylene glycol monobutyl
  • glycols include, but are not limited to, for example, ethylene glycol, propylene glycol, hexylene glycol, butanediol, glycerol, and the like, and mixtures thereof.
  • carboxylic acids include, but are not limited to, for example, unbranched saturated or unsaturated monocarboxylic acids: methanoic acid (formic acid), ethanoic acid (acetic acid), propanoic acid (propionic acid), pentanoic acid (valeric acid), hexanoic acid (caproic acid); branched saturated or unsaturated monocarboxylic acids: 2-methylpentanoic acid, 2-ethylhexanoic acid; unbranched saturated or unsaturated di- or tricarboxylic acids: propanedioic acid (malonic acid), butanedioic acid (succinic acid), pentanedioic acid (glutaric acid), hexanedioic acid (
  • alkaline examples include, but are not limited to, sodium hydroxide, potassium hydroxide, ammonium hydroxide, tetramethyl ammonium hydroxide, monoethanolamine, diethanolamine, triethanolamine, ammonium hydroxide, diethylamine, dimethylamine, trimethanolamine, butyldimethylamine, dibutylmethylamine, trihydroxyamine, monopropylamine, dipropylamine, tripropylamine, monopropanolamine, dipropanolamine, tripropanolamine, monoisopropanolamine, diisopropanolamine, triisopropanolamine, n-butylamine, t-butylamine, methylpropylamine, ethyldimethylamine, 2-amino-1,3-propanediol, 2-amino-2-methyl-1,3-propanediol, ethanolpropanolamine, 2-(butylamino)ethanol, 2-(cyclohexyla
  • the treatment stabilizer is typically added to the polysilazane waste in a ratio of treatment stabilizer to polysilazane waste of from about 1:2 to about 1:14 with ratios of about 1:4 to about 1:10, about 1:6 to about 1:9, and about 1:7 to about 1:9 also contemplated.
  • a carrier solvent for the treatment stabilizer is optional.
  • the present invention is related to a process for treating polysilazane waste comprising contacting the polysilazane waste with a treatment stabilizer selected from the group consisting of an OH-containing compound and an OH-containing compound and alkaline mixture.
  • the treatment stabilizer, or treatment stabilizer solution can contact the polysilazane waste by (a) injecting the treatment stabilizer into a waste stream of polysilazane waste; (b) adding the treatment stabilizer into a container containing polysilazane waste; or (c) adding the polysilazane waste into a container containing treatment stabilizer.
  • OH containing compound examples include, but are not limited to, for example, alcohols, ether alcohols, glycols, and carboxylic acids, and mixtures thereof.
  • alcohols include, but are not limited to, methanol, ethanol, n-propanol, isopropanol, n-butanol, sec-butanol, phenol, and the like.
  • ether alcohols include, but are not limited to, for example, 1-butoxyethoxy-2-propanol, 3-methyl-3-methoxybutanol, ethylene glycol n-butyl ether, ethylene glycol phenyl ether, ethylene glycol propyl ether, diethylene glycol hexyl ether, diethylene glycol monoethyl ether, diethylene glycol monomethyl ether, diethylene glycol monobutyl ether, diethylene glycol monopropyl ether, propylene glycol ethyl ether, propylene glycol isobutyl ether, propylene glycol monomethyl ether, propylene glycol monobutyl ether, propylene glycol monoethyl ether, propylene glycol n-propyl ether, propylene glycol phenyl ether, propylene glycol-t-butyl ether, dipropylene glycol ethyl ether, dipropylene glycol monobutyl
  • glycols include, but are not limited to, for example, ethylene glycol, propylene glycol, hexylene glycol, butanediol, glycerol, and the like, and mixtures thereof.
  • carboxylic acids include, but are not limited to, for example, unbranched saturated or unsaturated monocarboxylic acids: methanoic acid (formic acid), ethanoic acid (acetic acid), propanoic acid (propionic acid), pentanoic acid (valeric acid), hexanoic acid (caproic acid); branched saturated or unsaturated monocarboxylic acids: 2-methylpentanoic acid, 2-ethylhexanoic acid; unbranched saturated or unsaturated di- or tricarboxylic acids: propanedioic acid (malonic acid), butanedioic acid (succinic acid), pentanedioic acid (glutaric acid), hexanedioic acid (
  • alkaline examples include, but are not limited to, sodium hydroxide, potassium hydroxide, ammonium hydroxide, tetramethyl ammonium hydroxide, monoethanolamine, diethanolamine, triethanolamine, ammonium hydroxide, diethylamine, dimethylamine, trimethanolamine, butyldimethylamine, dibutylmethylamine, trihydroxyamine, monopropylamine, dipropylamine, tripropylamine, monopropanolamine, dipropanolamine, tripropanolamine, monoisopropanolamine, diisopropanolamine, triisopropanolamine, n-butylamine, t-butylamine, methylpropylamine, ethyldimethylamine, 2-amino-1,3-propanediol, 2-amino-2-methyl-1,3-propanediol, ethanolpropanolamine, 2-(butylamino)ethanol, 2-(cyclohexyla
  • the treatment stabilizer is typically added to the polysilazane waste in a ratio of treatment stabilizer to polysilazane waste of from about 1:2 to about 1:14 with ratios of about 1:4 to about 1:10, about 1:6 to about 1:9, and about 1:7 to about 1:9 also contemplated.
  • a carrier solvent for the treatment stabilizer is optional.
  • an OH containing compound e.g. alcohols, ether alcohols, glycols, carboxylic acids
  • a reaction initiator e.g. alkaline
  • the absolute degree of neutralization or stabilization may depend upon the relative activity, quantity and concentration of the OH containing compound alone or in conjunction with the reaction initiator mixture added.
  • the amount of the alkaline that is added to the OH containing compound ranges from about 2% to about 20%, based on the amount of the OH containing compound present.
  • OH containing compound examples include, but are not limited to, for example, alcohols, ether alcohols, glycols, and carboxylic acids, and mixtures thereof.
  • examples of the alcohol include, but are not limited to, methanol, ethanol, n-propanol, isopropanol, n-butanol, sec-butanol, phenol, and the like.
  • ether alcohols include, but are not limited to, for example, 1-butoxyethoxy-2-propanol, 3-methyl-3-methoxybutanol, ethylene glycol n-butyl ether, ethylene glycol phenyl ether, ethylene glycol propyl ether, diethylene glycol hexyl ether, diethylene glycol monoethyl ether, diethylene glycol monomethyl ether, diethylene glycol monobutyl ether, diethylene glycol monopropyl ether, propylene glycol ethyl ether, propylene glycol isobutyl ether, propylene glycol monomethyl ether, propylene glycol monobutyl ether, propylene glycol monoethyl ether, propylene glycol n-propyl ether, propylene glycol phenyl ether, propylene glycol-t-butyl ether, dipropylene glycol ethyl ether, dipropylene glycol monobutyl
  • glycols include, but are not limited to, for example, ethylene glycol, propylene glycol, hexylene glycol, butanediol, glycerol, and the like, and mixtures thereof.
  • carboxylic acids include, but are not limited to, for example, unbranched saturated or unsaturated monocarboxylic acids: methanoic acid (formic acid), ethanoic acid (acetic acid), propanoic acid (propionic acid), pentanoic acid (valeric acid), hexanoic acid (caproic acid); branched saturated or unsaturated monocarboxylic acids: 2-methylpentanoic acid, 2-ethylhexanoic acid; unbranched saturated or unsaturated di- or tricarboxylic acids: propanedioic acid (malonic acid), butanedioic acid (succinic acid), pentanedioic acid (glutaric acid), hexanedioic acid (
  • alkaline examples include, but are not limited to, sodium hydroxide, potassium hydroxide, ammonium hydroxide, tetramethyl ammonium hydroxide, monoethanolamine, diethanolamine, triethanolamine, ammonium hydroxide, diethylamine, dimethylamine, trimethanolamine, butyldimethylamine, dibutylmethylamine, trihydroxyamine, monopropylamine, dipropylamine, tripropylamine, monopropanolamine, dipropanolamine, tripropanolamine, monoisopropanolamine, diisopropanolamine, triisopropanolamine, n-butylamine, t-butylamine, methylpropylamine, ethyldimethylamine, 2-amino-1,3-propanediol, 2-amino-2-methyl-1,3-propanediol, ethanolpropanolamine, 2-(butylamino)ethanol, 2-(cyclohexyla
  • the carrier solvent is one which is not reactive with the polysilazane.
  • examples include hydrocarbon solvents (for example, tetrahydronaphthalene), ether acetates (for example, propylene glycol monomethyl ether acetate), and other similar solvents that do not react with polysilazane.
  • Some preferred embodiments contain a carrier solvent having a flash point greater than 140° F. to form a treatment stabilizer solution.
  • One of the benefits of the present invention is to allow for the disposal of the treated polysilazane waste as non-hazardous waste.
  • a treatment stabilizer comprising a carrier solvent and an alcohol and an alcohol and alkaline mixture
  • the flash point of the treated polysilazane waste when a high flash point carrier solvent is used, is greater than 140° F. This makes disposal simpler as the waste is now shipped as non-hazardous and becomes useful for fuel blending. Therefore, waste streams of solvent from other facilities, or even the same facility where polysilazane materials are coated, could be used as the carrier solvent, provided the flash point of the waste stream is greater than 140° F.
  • the potential for the unstabilized solution to off-gas causing pressurization of the drum potentially resulting in catastrophic drum failure is eliminated. Also since all the polysilazane waste is stabilized prior to the filling of the waste drums, the waste transferred to drums for disposal do not have to sit for a period of time to vent off gases that could build up if the present process was not used. Finally, the stabilized waste, if desired, could be disposed of by fuel blending for heat recovery rather than requiring it to be incinerated. The unstabilized waste, itself, is too unstable or reactive so cannot be disposed of by fuel blending. The cost to incinerate the waste is approximately three (3) times that of disposing of the waste by fuel blending.
  • the contact can occur in situ. That is, as the polysilazane waste is generated and placed into a holding tank, an amount of the treatment stabilizer is then added to the holding tank. Since the amount of the treatment stabilizer will be greater than the amount of the polysilazane waste, there will be intermixing without the need for a separate mixer.
  • the treatment stabilizer is added to the drum after the polysilazane waste is pumped into the drum or the drum is precharged with an amount of the treatment stabilizer, and then the drum contents are stirred.

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  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Sustainable Development (AREA)
  • Processing Of Solid Wastes (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Processes Of Treating Macromolecular Substances (AREA)
US11/419,009 2006-05-18 2006-05-18 Treatment of Polysilazane Waste Abandoned US20070270625A1 (en)

Priority Applications (10)

Application Number Priority Date Filing Date Title
US11/419,009 US20070270625A1 (en) 2006-05-18 2006-05-18 Treatment of Polysilazane Waste
TW96116743A TWI426095B (zh) 2006-05-18 2007-05-11 聚矽氮烷廢料之處理
EP20070734653 EP2024432B1 (en) 2006-05-18 2007-05-15 Treatment of polysilazane waste
KR20087028567A KR101402548B1 (ko) 2006-05-18 2007-05-15 폴리실라잔 폐기물의 처리
CNA2007800180426A CN101448885A (zh) 2006-05-18 2007-05-15 聚硅氨烷废料的处理
JP2009510569A JP5298337B2 (ja) 2006-05-18 2007-05-15 ポリシラザン廃棄物の処理
DE200760003350 DE602007003350D1 (de) 2006-05-18 2007-05-15 Behandlung von polysilazan-abfall
PCT/IB2007/001347 WO2007135556A1 (en) 2006-05-18 2007-05-15 Treatment of polysilazane waste
IL195004A IL195004A0 (en) 2006-05-18 2008-10-30 Treatment of polysilazane waste
MYPI20084652 MY144317A (en) 2006-05-18 2008-11-17 Treatment of polysilazane waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US11/419,009 US20070270625A1 (en) 2006-05-18 2006-05-18 Treatment of Polysilazane Waste

Publications (1)

Publication Number Publication Date
US20070270625A1 true US20070270625A1 (en) 2007-11-22

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ID=38441565

Family Applications (1)

Application Number Title Priority Date Filing Date
US11/419,009 Abandoned US20070270625A1 (en) 2006-05-18 2006-05-18 Treatment of Polysilazane Waste

Country Status (10)

Country Link
US (1) US20070270625A1 (ja)
EP (1) EP2024432B1 (ja)
JP (1) JP5298337B2 (ja)
KR (1) KR101402548B1 (ja)
CN (1) CN101448885A (ja)
DE (1) DE602007003350D1 (ja)
IL (1) IL195004A0 (ja)
MY (1) MY144317A (ja)
TW (1) TWI426095B (ja)
WO (1) WO2007135556A1 (ja)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7240022B1 (en) 1998-05-19 2007-07-03 Mypoints.Com Inc. Demographic information gathering and incentive award system and method
JP2018140318A (ja) * 2015-07-22 2018-09-13 コニカミノルタ株式会社 固化物、固化物の製造方法及び固化物の安定化方法

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5464918A (en) * 1991-10-07 1995-11-07 Lanxide Technology Company, Lp Peroxide-substituted polysilazanes
US6190788B1 (en) * 1998-06-24 2001-02-20 Tokyo Ohka Kogyo Co., Ltd. Method for the formation of a siliceous coating film
US6310168B1 (en) * 1997-08-08 2001-10-30 Tonen Corporation Aminated polysilazane and process for the preparation thereof
US20050027089A1 (en) * 2001-12-27 2005-02-03 Yasuo Shimizu Solvent for treating polysilazane and method of treating polysilazane with the solvent
US20050279255A1 (en) * 2002-11-01 2005-12-22 Tadashi Suzuki Polysilane-containing coating solution

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS572922A (en) * 1980-06-09 1982-01-08 Mitsubishi Heavy Ind Ltd Combusting method of waste oil
DE4134019A1 (de) * 1991-10-15 1993-04-22 Bayer Ag Reinigung von polycarbonat- und polyester-abfaellen
JP3283276B2 (ja) * 1991-12-04 2002-05-20 東燃ゼネラル石油株式会社 改質ポリシラザン及びその製造方法
JPH08279445A (ja) * 1995-04-07 1996-10-22 Tokyo Ohka Kogyo Co Ltd Ｓｏｇ膜形成方法
US5817183A (en) * 1996-08-12 1998-10-06 General Electric Company Method for removing coatings from thermoplastic substrates
JP2003100865A (ja) * 2001-09-21 2003-04-04 Catalysts & Chem Ind Co Ltd 半導体基板の製造方法および半導体基板
JP4543617B2 (ja) * 2002-04-22 2010-09-15 セイコーエプソン株式会社 アクティブマトリクス基板の製造方法、電気光学装置の製造方法、電子機器の製造方法、アクティブマトリクス基板の製造装置、電気光学装置の製造装置、及び電気機器の製造装置
JP4106684B2 (ja) * 2002-07-18 2008-06-25 光 恩藤 シリコーン撥水被覆の解除方法

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5464918A (en) * 1991-10-07 1995-11-07 Lanxide Technology Company, Lp Peroxide-substituted polysilazanes
US6310168B1 (en) * 1997-08-08 2001-10-30 Tonen Corporation Aminated polysilazane and process for the preparation thereof
US6190788B1 (en) * 1998-06-24 2001-02-20 Tokyo Ohka Kogyo Co., Ltd. Method for the formation of a siliceous coating film
US6338868B1 (en) * 1998-06-24 2002-01-15 Tokyo Ohka Kogyo Co., Ltd. Method for the formation of a siliceous coating film
US20050027089A1 (en) * 2001-12-27 2005-02-03 Yasuo Shimizu Solvent for treating polysilazane and method of treating polysilazane with the solvent
US20050279255A1 (en) * 2002-11-01 2005-12-22 Tadashi Suzuki Polysilane-containing coating solution

Also Published As

Publication number Publication date
EP2024432B1 (en) 2009-11-18
KR101402548B1 (ko) 2014-06-19
JP5298337B2 (ja) 2013-09-25
TW200804469A (en) 2008-01-16
WO2007135556A1 (en) 2007-11-29
CN101448885A (zh) 2009-06-03
IL195004A0 (en) 2009-08-03
KR20090018921A (ko) 2009-02-24
JP2009537305A (ja) 2009-10-29
TWI426095B (zh) 2014-02-11
EP2024432A1 (en) 2009-02-18
MY144317A (en) 2011-08-29
DE602007003350D1 (de) 2009-12-31

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