CN111229023B - Chemical degradation additive - Google Patents

Chemical degradation additive Download PDF

Info

Publication number
CN111229023B
CN111229023B CN201811439273.0A CN201811439273A CN111229023B CN 111229023 B CN111229023 B CN 111229023B CN 201811439273 A CN201811439273 A CN 201811439273A CN 111229023 B CN111229023 B CN 111229023B
Authority
CN
China
Prior art keywords
chemical degradation
hepes
nanogold
weight
parts
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.)
Active
Application number
CN201811439273.0A
Other languages
Chinese (zh)
Other versions
CN111229023A (en
Inventor
邹晓虎
文起东
崔俊峰
文博
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.)
Inner Mongolia Dongsheng Diatomite Technology Innovation Industrial Park Co ltd
Original Assignee
Inner Mongolia Dongsheng Diatomite Technology Innovation Industrial Park Co ltd
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 Inner Mongolia Dongsheng Diatomite Technology Innovation Industrial Park Co ltd filed Critical Inner Mongolia Dongsheng Diatomite Technology Innovation Industrial Park Co ltd
Priority to CN201811439273.0A priority Critical patent/CN111229023B/en
Publication of CN111229023A publication Critical patent/CN111229023A/en
Application granted granted Critical
Publication of CN111229023B publication Critical patent/CN111229023B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09DCOATING COMPOSITIONS, e.g. PAINTS, VARNISHES OR LACQUERS; FILLING PASTES; CHEMICAL PAINT OR INK REMOVERS; INKS; CORRECTING FLUIDS; WOODSTAINS; PASTES OR SOLIDS FOR COLOURING OR PRINTING; USE OF MATERIALS THEREFOR
    • C09D7/00Features of coating compositions, not provided for in group C09D5/00; Processes for incorporating ingredients in coating compositions
    • C09D7/40Additives
    • C09D7/60Additives non-macromolecular
    • C09D7/61Additives non-macromolecular inorganic
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09DCOATING COMPOSITIONS, e.g. PAINTS, VARNISHES OR LACQUERS; FILLING PASTES; CHEMICAL PAINT OR INK REMOVERS; INKS; CORRECTING FLUIDS; WOODSTAINS; PASTES OR SOLIDS FOR COLOURING OR PRINTING; USE OF MATERIALS THEREFOR
    • C09D7/00Features of coating compositions, not provided for in group C09D5/00; Processes for incorporating ingredients in coating compositions
    • C09D7/40Additives
    • C09D7/60Additives non-macromolecular
    • C09D7/63Additives non-macromolecular organic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/80Type of catalytic reaction
    • B01D2255/802Photocatalytic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/708Volatile organic compounds V.O.C.'s

Abstract

The invention relates to a chemical degradation additive, belonging to the field of chemical degradation or photocatalytic additives. The invention provides a chemical degradation additive, which comprises HEPES and nanogold. The present invention can greatly increase the speed and the amount of chemical degradation. The invention has the following technical effects: by using the chemical degradation additive, the chemical degradation rate can be greatly improved, and the air pollution treatment is facilitated.

Description

Chemical degradation additive
Technical Field
The invention relates to a chemical degradation additive, belonging to the field of chemical degradation or photocatalytic additives.
Background
People often suffer from pollution of interior decoration materials, and the decoration materials are not environment-friendly, can cause pollution to the interior environment and harm human health. In order to treat air pollution, people generally adsorb harmful gases by physical adsorption or chemical degradation. However, the chemical degradation method in the prior art has low efficiency and slow degradation speed, and therefore, it is urgently needed to find an additive which can greatly enhance the rate of chemical degradation.
Disclosure of Invention
The object of the present invention is to overcome the disadvantages of the prior art measures and to provide a chemical degradation additive which allows a substantial increase in the rate and amount of chemical degradation.
In order to achieve the object of the present invention, the present invention provides a chemical degradation additive comprising HEPES and nanogold.
Further, in the above chemical degradation additive, the HEPES is 10-100 mmol per liter.
Further, in the chemical degradation additive, the HEPES is 100 millimoles per liter, and the nano gold is 0.1-5 nanomoles per liter.
Further, in the chemical degradation additive, the nano gold is 5 nanomole per liter.
Further, the chemical degradation additive also comprises titanium dioxide.
The invention has the following technical effects: by using the chemical degradation additive, the chemical degradation rate can be greatly improved, and the air pollution treatment is facilitated.
Drawings
FIG. 1 shows the concentration of nanogold and H in the present invention2O2And generating a graph of the relation of the relative quantity.
Detailed Description
The following examples are intended to illustrate the invention but are not intended to limit the scope of the invention. Unless otherwise specified, the technical means used in the examples are conventional means well known to those skilled in the art, and the raw materials used are commercially available products.
In order to remove organic pollutants from indoor environments, diatomaceous earth is generally used for physical adsorption. Diatomaceous earth is a rock pile formed by settling in a marine lake by plant plankton belonging to algae. The unicellular plant biological algae can unusually absorb silicate in water to form porous cell wall, and the remains precipitate and petrifaction to form 'diatomite' with silicic acid as main component. The microporous structure ensures that the diatomite has good absorption effect on harmful gases such as organic pollutants and the like in the indoor environment. However, the greatest problem with physical adsorption is the presence of saturation. Therefore, the organic pollutants adsorbed in the diatomite must be chemically degraded to treat the harmful gases more thoroughly and keep the environment clean. The search for an efficient additive to promote the rate of chemical degradation or photocatalysis is a problem that needs to be solved urgently. The inventor finds that the nanogold has a good effect of promoting chemical degradation or photocatalysis on HEPES (4-hydroxyethyl piperazine ethanesulfonic acid) through multiple experiments. HEPES can be fixed at 10-100 mmoles per liter for the experiments.
Table 1 below shows the H produced at a constant concentration of nano-gold in HEPES2O2In relation to the relative amount ofExperimental data.
TABLE 1
Figure GDA0003326840240000031
As shown in Table 1, H2O2Is proportional to the amount of HEPES oxidation product produced, which has a characteristic absorption peak at 350 nanometers (nm), so that H can be measured by measuring the intensity of the characteristic absorption peak at 350nm with an ultraviolet-visible spectrophotometer2O2Relative production amount of (2).
The data in Table 1 show that the higher the concentration of nanogold, the higher the concentration of HEPES, the more H is generated at a constant HEPES concentration2O2The greater the relative amount of (a). FIG. 1 shows the concentration of nanogold and H in the present invention2O2Generating a graph of the relation of relative quantity, in FIG. 1, series 1 represents the concentration of the nano-gold, series 2 represents H2O2Generating relative quantities. As can be seen from the figure, the concentration of the nano-gold is substantially equal to that of H2O2A proportional relationship of relative quantities is generated. Organic pollutants adsorbed by diatomite are easier to be H2O2And oxidative degradation. HEPES is a photosensitive material that can chemically degrade or photo-catalyze organic contaminants. Thus, the chemical degradation or photocatalytic capacity of HEPES can be enhanced by adding nanogold. Therefore, organic pollutants adsorbed by the diatomite can be quickly separated from H by adding certain amounts of HEPES and nanogold to the diatomite material2O2And oxidative degradation.
Table 2 below shows a comparison of the ability of the diatomaceous earth material to oxidatively degrade formaldehyde after addition of HEPES and nanogold (0.5 cubic meters in a glass-sealed test chamber with half an hour degradation time).
TABLE 2
Figure GDA0003326840240000032
Figure GDA0003326840240000041
As shown in table 2 above, the ability of the diatomite material to oxidatively degrade formaldehyde after adding HEPES and nanogold is greatly enhanced with the increase of the nanogold concentration.
In addition, the nanogold can chemically degrade organic pollutants adsorbed by the diatomite.
Generally, titanium dioxide is a photocatalyst, and can be used for photocatalytic degradation of organic pollutants under illumination conditions. Meanwhile, HEPES and nanogold are added, so that organic pollutants can be degraded in a better photocatalytic manner under the illumination condition, and can also be degraded under the condition without illumination.
In one embodiment of the present invention, the diatomite layer may include 50-60 parts by weight of diatomite and 0.0000001-0.01 part by weight of nano gold.
In another embodiment of the present invention, the diatomite layer may include 50-60 parts by weight of diatomite, 0.1-5 parts by weight of HEPES, and 0.0000001-0.01 parts by weight of nanogold.
In still another embodiment of the present invention, the diatomite layer may include 50-60 parts by weight of diatomite, 5-10 parts by weight of titanium dioxide, 0.1-5 parts by weight of HEPES, 0.0000001-0.01 parts by weight of nanogold.
In still another embodiment of the present invention, the diatomite layer may include 50-60 parts by weight of diatomite, 10-15 parts by weight of plant fiber, 5-10 parts by weight of bentonite, 5-10 parts by weight of titanium dioxide, 0.1-5 parts by weight of HEPES, 0.0000001-0.01 parts by weight of nanogold.
In addition, the diatomite layer can also comprise 1-15 parts by weight of foaming agent.
Regarding the preparation of the adsorbing material, specifically, firstly, 50 to 60 parts by weight of diatomite, 10 to 15 parts by weight of plant fiber and 5 to 10 parts by weight of bentonite are put into a dispersion machine for dispersion treatment; then adding 1-15 parts by weight of a foaming agent to stir for sufficient dissolution to obtain a diatomaceous earth dispersion; then, 5-10 parts by weight of titanium dioxide, 0.1-5 parts by weight of HEPES and/or 0.0000001-0.01 parts by weight of nanogold may be added. Finally, a copolymer emulsion of vinyl versatate manufactured by UK Shell chemical company was added to prepare a diatomaceous earth paint.
The diatomite coating can be coated on the outer sides of a toilet bowl body, a bathtub and a cabinet plate of a bathroom cabinet made of acrylic materials to form diatomite layers, so that organic pollutants are chemically degraded.
The above description is only a preferred embodiment of the present invention and should not be taken as limiting the invention, and any modifications, equivalents and improvements made within the spirit and scope of the present invention should be included.

Claims (4)

1. A chemical degradation additive, which is characterized by comprising diatomite, HEPES and nanogold, wherein the HEPES is 10-100 millimoles per liter, and the nanogold is 0.1-5 nanomoles per liter.
2. The chemical degradation additive according to claim 1, wherein the HEPES is 100 mmole per litre.
3. The chemical degradation additive of claim 2, wherein the nanogold is 5 nanomoles per liter.
4. The chemical degradation additive of claim 3 further comprising titanium dioxide.
CN201811439273.0A 2018-11-29 2018-11-29 Chemical degradation additive Active CN111229023B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811439273.0A CN111229023B (en) 2018-11-29 2018-11-29 Chemical degradation additive

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811439273.0A CN111229023B (en) 2018-11-29 2018-11-29 Chemical degradation additive

Publications (2)

Publication Number Publication Date
CN111229023A CN111229023A (en) 2020-06-05
CN111229023B true CN111229023B (en) 2022-01-28

Family

ID=70863124

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811439273.0A Active CN111229023B (en) 2018-11-29 2018-11-29 Chemical degradation additive

Country Status (1)

Country Link
CN (1) CN111229023B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0962526A2 (en) * 1998-05-29 1999-12-08 QIAGEN GmbH Method for reversible modification of thermostable enzymes
CN1526732A (en) * 1999-01-30 2004-09-08 \ Process for producing high pureness albumin solution
CN1798840A (en) * 2003-03-19 2006-07-05 比奥根艾迪克Ma公司 NOGO receptor binding protein.
CN102170903A (en) * 2008-05-02 2011-08-31 癌症研究技术有限公司 Products and methods for stimulating an immune response
CN103201008A (en) * 2010-08-06 2013-07-10 莫利康普矿物有限责任公司 Agglomeration of high surface area rare earths

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0962526A2 (en) * 1998-05-29 1999-12-08 QIAGEN GmbH Method for reversible modification of thermostable enzymes
CN1526732A (en) * 1999-01-30 2004-09-08 \ Process for producing high pureness albumin solution
CN1798840A (en) * 2003-03-19 2006-07-05 比奥根艾迪克Ma公司 NOGO receptor binding protein.
CN102170903A (en) * 2008-05-02 2011-08-31 癌症研究技术有限公司 Products and methods for stimulating an immune response
CN103201008A (en) * 2010-08-06 2013-07-10 莫利康普矿物有限责任公司 Agglomeration of high surface area rare earths

Also Published As

Publication number Publication date
CN111229023A (en) 2020-06-05

Similar Documents

Publication Publication Date Title
Belhouchet et al. Photocatalytic degradation of tetracycline antibiotic using new calcite/titania nanocomposites
Ma et al. Model-based evaluation of tetracycline hydrochloride removal and mineralization in an intimately coupled photocatalysis and biodegradation reactor
Syngouna et al. Inactivation of MS2 bacteriophage by titanium dioxide nanoparticles in the presence of quartz sand with and without ambient light
Bouras et al. Photocatalytic oxidation of azo dye solutions by impregnation of ZnO on fungi
Peighambardoust et al. Sono-photocatalytic activity of sea sediment@ 400/ZnO catalyst to remove cationic dyes from wastewater
Ngoh et al. Fabrication and properties of an immobilized P25TiO2-montmorillonite bilayer system for the synergistic photocatalytic–adsorption removal of methylene blue
CN104673019A (en) Coating
Nawaz et al. Solar light driven degradation of textile dye contaminants for wastewater treatment–studies of novel polycationic selenide photocatalyst and process optimization by response surface methodology desirability factor
CN204162465U (en) A kind of water treatment device based on photocatalysis composite ceramic separation membrane
Simon et al. Seawater disinfection by chlorine dioxide and sodium hypochlorite. A comparison of biofilm formation
Moussavi et al. Removal of acid orange 7 dye from synthetic textile wastewater by single-walled carbon nanotubes: adsorption studies, isotherms and kinetics
JP2008221113A (en) Floating photocatalyst and polluted water treatment method using the same
Liu et al. Hybrid persulfate/sonocatalysis for degradation of acid orange 7 in the presence of Ag2O/CuWO4 composite: operating parameters and sonocatalytic mechanism
CN111229023B (en) Chemical degradation additive
Abdi et al. Application of a hybrid enzymatic and photo-fenton process for investigation of azo dye decolorization on TiO2/metal-foam catalyst
KR100793641B1 (en) Apparatus for treating water by boll of titaninum zeolite biofilm and recipe
Talaiekhozani et al. Comparing the ZnO/Fe (VI), UV/ZnO and UV/Fe (VI) processes for removal of Reactive Blue 203 from aqueous solution
CN111234569B (en) Diatomite coating, preparation method thereof and decorative plate made of diatomite coating
Cheng et al. Enhanced degradation effect of nano-PAA–CuCl2 with controllable 3D structure as heterogeneous Fenton-like catalyst over a wide pH range
JP2009189914A (en) Microorganism-carrying photocatalyst-containing sintered body for water purification and its manufacturing method, and method for purifying water in water area using the sintered body and water purification process of water area using it
CN111320775A (en) Manufacturing method of environment-friendly closestool
Reddy et al. Photocatalytic disinfection of Escherichia coli over titanium (IV) oxide supported on Hβ zeolite
Alkaim et al. Adsorption and photocatalytic degradation of pharmaceutical amoxicillin using TiO2 nanoparticles in aqueous solutions: oxidative coupling as spectrophotometric method
CN111227683B (en) Environment-friendly bathroom cabinet
Baklavaridis et al. Recent progress in the advanced oxidation of wastewaters using recycled fly ashes as alternative catalytic agents

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant