CN108579689A - A kind of beta cyclo dextrin polymer and preparation and the method for handling anionic dye waste water using it - Google Patents

A kind of beta cyclo dextrin polymer and preparation and the method for handling anionic dye waste water using it Download PDF

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Publication number
CN108579689A
CN108579689A CN201810356041.2A CN201810356041A CN108579689A CN 108579689 A CN108579689 A CN 108579689A CN 201810356041 A CN201810356041 A CN 201810356041A CN 108579689 A CN108579689 A CN 108579689A
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beta
methyl orange
cyclo dextrin
dextrin polymer
preparation
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江洪流
高伟
谢小林
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Nanchang Hangkong University
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Nanchang Hangkong University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08BPOLYSACCHARIDES; DERIVATIVES THEREOF
    • C08B37/00Preparation of polysaccharides not provided for in groups C08B1/00 - C08B35/00; Derivatives thereof
    • C08B37/0006Homoglycans, i.e. polysaccharides having a main chain consisting of one single sugar, e.g. colominic acid
    • C08B37/0009Homoglycans, i.e. polysaccharides having a main chain consisting of one single sugar, e.g. colominic acid alpha-D-Glucans, e.g. polydextrose, alternan, glycogen; (alpha-1,4)(alpha-1,6)-D-Glucans; (alpha-1,3)(alpha-1,4)-D-Glucans, e.g. isolichenan or nigeran; (alpha-1,4)-D-Glucans; (alpha-1,3)-D-Glucans, e.g. pseudonigeran; Derivatives thereof
    • C08B37/0012Cyclodextrin [CD], e.g. cycle with 6 units (alpha), with 7 units (beta) and with 8 units (gamma), large-ring cyclodextrin or cycloamylose with 9 units or more; Derivatives thereof
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents

Abstract

A kind of method for handling waste water from dyestuff the invention discloses beta cyclodextrin polymer and its preparation and using it.Preparation method includes the following steps:In an inert atmosphere, by beta cyclodextrin (β CD), crosslinking agent (tetrafluoro terephthalonitrile, TFPN after), alkaline salt compound carries out polymerisation in organic solvent, resulting polymers are reacted with ethanol amine (EA) again, and reaction product obtains porous beta cyclodextrin (EA CDP).Porous beta cyclodextrin prepared by the present invention can quickly remove the anionic dyes pollutant such as methyl orange, methyl orange, acid blue 83, Indian yellow G in water removal, and adsorbing filament technique specific activity Carbon Materials are big and price is low.In addition, polymer can regenerate for several times in a mild condition, and performance loss very little.

Description

A kind of beta cyclo dextrin polymer and preparation and handle anionic dye waste water using it Method
Technical field
The invention belongs to Dye Adsorption technical field in wastewater treatment, more particularly to prepared by a kind of anionic dye adsorbent With the method for handling anionic dye waste water using it.
Background technology
Water pollution problems becomes increasingly conspicuous in recent years, and an important pollution sources of the waste water from dyestuff as water pollution are greatly endangered Ecological environment and health, such as the anionic dyes such as common methyl orange, Congo red, acid blue 83, Indian yellow G have been done harm to, Since its is difficult to degrade, bio-toxicity is high, being discharged into after water body not only can directly endanger the growth of aquatic animals and plants, destroy soil, and And health can be damage by bioconcentration.Currently, mainly having absorption, chemistry heavy in the processing method of waste water from dyestuff Shallow lake, UF membrane, bioanalysis etc., wherein the method for absorption and UF membrane due to it is efficient, simple for process, do not generate secondary pollution etc. Feature has obtained the extensive concern of domestic and foreign scholars.
Go in water removal organic dye pollutant the most commonly used is activated carbon, but activated carbon has several defects, including absorption speed Degree is slow, expensive, and is difficult to remove the micropollutants of many relative hydropathics.In addition, regeneration waste active carbon energy consumption is high, and The absorption property of regenerated carbon is poor.
In conclusion in existing commercial Application technology, absorption method, which handles waste water from dyestuff, still has prodigious advantage, and inhales Adsorbent used in during attached method processing waste water is still not up to ideal effect, the new dye absorption of excellent combination property The research and development of agent are still the hot and difficult issue of the current technical field research work.
Cyclodextrin as second generation super molecular compound has inner cavity hydrophobic, and the hydrophilic special construction of outer rim makes it can It is formed with many organic and inorganic molecule according to Van der Waals force, hydrophobic interaction power, the intermolecular matching effect of Subjective and Objective etc. Inclusion compound and molecular assembled system become chemistry and the interested research object of chemical research person.This selective envelope is made It is protected in Chemical Decomposition, organic synthesis and catalysis, drug control, food processing, environment with i.e. usually said molecular recognition function It is used widely in the fields such as shield and nano material.Since the solubility of β-CD is smaller, in order to overcome cyclodextrin solubility itself Defect, natural cyclodextrin is modified causes greatly to pay attention in recent years.Cyclodextrin is organic with being captured from gas, liquid The ability of molecule and complexation of metal ions, the polymer material containing cyclodextrin is in terms of the environmental protection such as environmental monitoring and wastewater treatment There is important application, thus prepares polymer using cyclodextrine derivatives and be expected to obtain the higher new material of stability.β-ring paste Essence is a kind of cheap, reproducible glucose products, and micropollutants can be adsorbed from water.Beta-cyclodextrin can be formed with pollutant Host-guest complex, but so far, compared with conventional activated carbon, the crosslinked beta cyclo dextrin polymer surface area reported Low, absorption property is poor.
Invention content
It is an object of the invention to the deficiencies for existing beta cyclo dextrin polymer adsorbent, provide a kind of efficiently removal The beta cyclo dextrin polymer sorbent preparation method of anionic dye and the side using its processing anionic dye waste water in waste water Method.
The technical solution adopted by the present invention is as follows:Anionic dye adsorbent, the adsorbent are beta cyclo dextrin polymer, Preparation includes the following steps:In nitrogen or argon gas, beta-cyclodextrin, crosslinking agent, alkali compounds are carried out in organic solvent After polymerisation, resulting polymers are reacted with ethanol amine again, and reaction finishes to obtain the beta cyclo dextrin polymer (EA- CDP)。
The crosslinking agent is for tetrafluoro terephthalonitrile or to itrile group ptfe pyridine;The alkali compounds is K2CO3Or KHCO3;The solvent is the organic solvent that tetrahydrofuran mixes composition with N,N-dimethylformamide;The tetrahydrofuran and N, The volume ratio of dinethylformamide is 7-10 ﹕ 1.
The mass ratio of the alkali compounds and beta-cyclodextrin is 3-5 ﹕ 1;The weight ratio of the beta-cyclodextrin and crosslinking agent For 2-3 ﹕ 1;The weight ratio of the ethanol amine and beta-cyclodextrin is 1 ﹕ 1-3 or 1 ﹕ 2.
In the substitution reaction step, temperature is 80-100 DEG C;The time of first time substitution reaction is 24-48 hours; The time of second secondary response is 24-48 hours;The substitution reaction carries out in argon gas or nitrogen atmosphere.
The method further includes following steps:After second of reaction step, reaction system is cooling, filtering, After removing remaining alkali compounds, obtained solid is washed with deionized, is dried in vacuo and obtains flaxen powdered sample Product.
It is a kind of using the anionic dye (methyl orange dye adsorbent) handle methyl orange dye waste water method its It is characterized in that:Methyl orange dye adsorbent is added in the waste water solution containing methyl orange dye, is made using oscillator concussion Methyl orange dye adsorbent fully adsorbs methyl orange, is then separated by filtration, and removes the beta cyclo dextrin polymer suction for having adsorbed dyestuff Attached dose.
The purpose of the present invention is achieved through the following technical solutions:
One of the objects of the present invention is to provide a kind of beta cyclo dextrin polymers with good adsorption function for invention content.
Another object of the present invention is to provide the preparation methods of above-mentioned polymer.
The third object of the present invention is to provide application of the beta cyclo dextrin polymer in dying industrial wastewater processing.
The present invention realizes that process is as follows:It is prepared by beta cyclo dextrin polymer (EA-CDP) shown in FIG. 1.
The preparation method of beta cyclo dextrin polymer (EA-CDP) of the present invention includes:
1, the preparation of CDP;
2, the preparation of beta cyclo dextrin polymer (EA-CDP).
Preparation method includes the following steps:In an inert atmosphere, by beta-cyclodextrin (β-CD), (tetrafluoro is to benzene two for crosslinking agent Nitrile, TFPN), after alkaline salt compound carries out polymerisation in organic solvent, resulting polymers again with ethanol amine (EA) progress Reaction, reaction product obtain porous beta cyclo dextrin polymer (EA-CDP).In the above method, the crosslinking agent is tetrafluoro to benzene two Formonitrile HCN or to formonitrile HCN base ptfe pyridine;The alkali compounds is K2CO3Or KHCO3;The solvent is tetrahydrofuran and dimethyl The mixed solvent of formamide (DMF) composition;The volume ratio of the tetrahydrofuran and n,N-Dimethylformamide is 6-10 ﹕ 1, specifically Can be 9 ﹕ 1.The mass ratio of the alkali compounds and beta-cyclodextrin is 3-5 ﹕ 1;The weight ratio of the beta-cyclodextrin and crosslinking agent For 2-3 ﹕ 1.The tetrafluoro terephthalonitrile is 1 to the weight ratio of formonitrile HCN base ptfe pyridine and beta-cyclodextrin:1-3 specifically may be used For 1 ﹕ 2;In the substitution reaction step, temperature is 60-120 DEG C, concretely 90 DEG C;The time of polymerisation is 24~48 Hour, concretely 24 hours;The reaction carries out in inert atmosphere such as nitrogen or argon gas atmosphere.Wherein, the removing The method that remaining alkali compounds can use salt acid elution;The concentration of hydrochloric acid used concretely 1mol/L;The cleaning solvent Selected from least one of deionized water, tetrahydrofuran and dichloromethane;Three kinds of solvents are washed with arbitrary tandem;Institute It states and dry be followed successively by vacuum freeze drying and obtain faint yellow solid powder CDP;Wherein, in the freeze-drying step, drying temperature Can be 77K;Concretely 15-30 minutes drying time more specifically can be 15 minutes.230mg is added in 100mL three-necked flasks CDP, the ethanol amine of 20mL is injected in the environment of nitrogen, and 120 DEG C of reaction temperature stirs 48h.Ethyl alcohol stirring is added after reaction 15min, obtained product filters and uses distillation washing three times, and is put into vacuum drying chamber drying for 24 hours, obtains product EA modifications Cyclodextrin (EA-CDP) in addition, the beta cyclo dextrin polymer being prepared according to the method described above and the polymer in water Processing adsorpting anion ionic dye also belongs to protection scope of the present invention.
Compared with the prior art, the advantages of the present invention are as follows:(1) adsorbent provided by the invention has higher specific surface Long-pending and lower cost, and environmental-friendly, it is with good stability under neutral or acid condition the features such as.(2) of the invention The anionic dye adsorbent can be obviously improved the performance of its Adsorption anionic dye methyl orange, reach efficient removal The purpose of methyl orange.Polymer material 3h can reach adsorption equilibrium, the removal rate of methyl orange dye up to 95.0% or more, Maximal absorptive capacity is up to 290mg/g.(3) beta cyclo dextrin polymer adsorbent provided by the invention removes anionic dye methyl orange Method have and be not necessarily to special installation, step is simple and efficient, will not introduce other harmful substances in processing procedure, the rate of adsorption compared with Quickly, the features such as adsorption efficiency is high.
Description of the drawings
Beta cyclo dextrin polymer (EA-CDP) shown in FIG. 1 prepares figure.
Fig. 2 is the infared spectrum of 1 gained EA-CDP of embodiment.
Fig. 3 is the nuclear magnetic spectrogram of 1 gained EA-CDP of embodiment.
Fig. 4 is adsorption time under difference EA-CDP additions in the processing example of methyl orange anionic dye waste water and absorption The graph of relation of amount.
Fig. 5 is the graph of relation of the methyl orange dye waste water for testing one handled in example between pH and adsorbance.
Fig. 6 is the absorption schematic diagram that beta cyclo dextrin polymer adsorbs methyl orange.
Specific implementation mode
With reference to specific embodiment, the present invention is further elaborated.The beta cyclo dextrin polymer adsorbent method is such as No special instruction is conventional method.The raw material can obtain unless otherwise instructed from open commercial sources.
The method for handling the waste water solution containing methyl orange dye furthermore with beta cyclo dextrin polymer adsorbent:By β-ring Dextrin polymer is added in the waste water solution containing methyl orange anionic dye, and shaken after mixing makes adsorbent fill for a period of time Divide absorption methyl orange dye, be then separated by filtration, removes the beta cyclo dextrin polymer absorption for having adsorbed methyl orange anionic dye Agent.Utilize the determination of methyl orange dye adsorbent Adsorption methyl orange anionic dye condition:By setting different absorption Time, different adsorbent input amounts, adsorption temp, the initial concentration of methyl orange, draws the suction of adsorbent in Methyl Orange in Wastewater Attached amount qtWith adsorption time t, initial concentration solution C0Etc. factors variation diagram, investigate beta cyclo dextrin polymer removal methyl orange Optimal adsorption condition.When visible light photometry being used to measure a certain etching solution in wavelength for the absorbance A at 464nm, according to C= KA calculates its concentration, and K is absorptivity (L/mol), the removal rate of methyl orange is then calculated according to (1) formula, according to (2) formula Calculate the adsorbance of adsorbent.
Wherein:E is the removal rate of methyl orange, qtFor the adsorbance (mg/g) of adsorbent, C0For the initial dense of methyl orange solution It spends (mg/L), CtFor the concentration (mg/L) of methyl orange in solution after absorption, V is the volume (L) of the methyl orange solution for absorption, M is the quality (g) that beta cyclo dextrin polymer is added.
Embodiment 1 prepares beta cyclo dextrin polymer (EA-CDP)
By 0.962g beta-cyclodextrins, 0.5g crosslinking agent tetrafluoro terephthalonitriles and 1.23g basic salt compound Ks2CO3It is added to 27ml tetrahydrofurans (THF) and 3mlN, dinethylformamide (DMF) in the mixed solvent (VTHF:VDMF=9), lead to nitrogen 5 to divide Clock carried out polymerisation after 48 hours at 85 DEG C, with the solid on 1mol/L salt acid elution filter paper, remove remaining K2CO3, Until CO2Release finishes, and washs obtained solid with 20ml deionized waters, 20ml tetrahydrofurans, 20ml dichloromethane successively, then will Solid is freeze-dried 10-20 minutes in high vacuum liquid nitrogen bath, is then dried in vacuo 2-3 days at room temperature, is obtained the first stepping Beta cyclo dextrin polymer CDP after row substitution reaction.230mgCDP made from above-mentioned experiment is taken, is injected in the environment of nitrogen The EA of 20mL, 120 DEG C of reaction temperature stir 48h.Ethyl alcohol is added after reaction and stirs 15min, obtained product, which filters, to be used in combination Distillation washing three times, and is put into vacuum drying chamber drying for 24 hours, obtains the amine-modified cyclodextrin polymerization (EA-CDP) of product ethanol. The infrared spectrum of the polymer is as shown in Fig. 2, nuclear magnetic spectrogram is as shown in Figure 3.As seen from the figure, the correct of the polymer architecture
Embodiment 2, EA-CDP absorption methyl orange experiments
1 gained beta cyclo dextrin polymer EA-CDP and 10ml initial concentration 30mg/l methyl orange solutions of 10mg embodiments are mixed It closes, is placed in 30 DEG C of constant temperature water bath oscillator with 170rmin-1Speed shake 30 minutes.After concussion, use 0.2 μm of polytetrafluoroethylene (PTFE) filter paper filters separation solid and solution.Pass through first in UV-vis ultraviolet visible spectrometry determination samples The residual concentration (measuring the absorbance A that wavelength is the places 464nm) of base orange, in 2 hours removable water Methylene Blue up to 95% with On.Ultrasonic beta-cyclodextrin compound, renewable beta-cyclodextrin compound, experiment cycle 5 times, not having property of polymer are impregnated with ethyl alcohol The loss of energy is smaller.
Embodiment 3, EA-CDP adsorb Congo Red test
The 1 Congo red solution of gained beta cyclo dextrin polymer EA-CDP and 10ml initial concentrations 30mg/l of 3mg embodiments is mixed It closes, is placed in 30 DEG C of constant temperature water bath oscillator with 170rmin-1Speed shake 30 minutes.After concussion, use 0.2 μm of polytetrafluoroethylene (PTFE) filter paper filters separation solid and solution.By rigid in UV-vis ultraviolet visible spectrometry determination samples The residual concentration (it is the absorbance A at 497nm to measure wavelength) of arnotto, can remove Congo red up to 95% or more in water in 2 hours. Ultrasonic beta-cyclodextrin compound is impregnated with ethyl alcohol, renewable beta-cyclodextrin compound, experiment cycle 5 times, polymer does not have performance Loss is smaller.
Embodiment 4, EA-CDP absorption acid blues 83 are tested
By 1 gained beta cyclo dextrin polymer EA-CDP of 3mg embodiments and 83 solution of 10ml initial concentration 30mg/l acid blues Mixing, is placed in 30 DEG C of constant temperature water bath oscillator with 170rmin-1Speed shake 30 minutes.After concussion, use 0.2 μm of polytetrafluoroethylene (PTFE) filter paper filters separation solid and solution.By sour in UV-vis ultraviolet visible spectrometry determination samples Property indigo plant 83 residual concentration (measuring the absorbance A that wavelength is the places 600nm), acid blue 8390% in removable water in 100 minutes. Ultrasonic beta-cyclodextrin compound, the renewable polymer, experiment cycle 3 times, beta cyclo dextrin polymer adsorptivity are impregnated with ethyl alcohol The loss of energy is smaller.
Embodiment 4, EA-CDP absorption Indian yellow G experiments
1 gained beta cyclo dextrin polymer EA-CDP and 10ml initial concentration 30mg/l Indian yellow G solution of 3mg embodiments is mixed It closes, is placed in 30 DEG C of constant temperature water bath oscillator with 170rmin-1Speed shake 30 minutes.After concussion, use 0.2 μm of polytetrafluoroethylene (PTFE) filter paper filters separation solid and solution.By sour in UV-vis ultraviolet visible spectrometry determination samples Property Huang G residual concentration (measuring the absorbance A that wavelength is the places 410nm), in 60 minutes in removable water Indian yellow G 95% with On.Ultrasonic beta-cyclodextrin compound, the renewable polymer, experiment cycle 5 times, beta cyclo dextrin polymer absorption are impregnated with ethyl alcohol Performance loss is smaller.

Claims (6)

1. anionic dye adsorbent, which is beta cyclo dextrin polymer, and preparation includes the following steps:In nitrogen or argon In gas, after beta-cyclodextrin, crosslinking agent, alkali compounds are carried out polymerisation in organic solvent, resulting polymers again with second Hydramine is reacted, and reaction finishes to obtain the beta cyclo dextrin polymer (EA-CDP).
2. anionic dye adsorbent according to claim 1, it is characterised in that:The crosslinking agent is tetrafluoro terephthaldehyde Nitrile or to itrile group ptfe pyridine;The alkali compounds is K2CO3Or KHCO3;The solvent is tetrahydrofuran and N, N- dimethyl The organic solvent of formamide mixing composition;The volume ratio of the tetrahydrofuran and N,N-dimethylformamide is 7-10 ﹕ 1.
3. the beta cyclo dextrin polymer preparation method according to claim 1-2, it is characterised in that:The alkali compounds with The mass ratio of beta-cyclodextrin is 3-5 ﹕ 1;The weight ratio of the beta-cyclodextrin and crosslinking agent is 2-3 ﹕ 1;The ethanol amine and β-ring The weight ratio of dextrin is 1 ﹕ 1-3 or 1 ﹕ 2.
4. according to any beta cyclo dextrin polymer preparation method in claim 1-3, it is characterised in that:The substitution is anti- It answers in step, temperature is 80-100 DEG C;The time of first time substitution reaction is 24-48 hours;The time of second secondary response is 24-48 hours;The substitution reaction carries out in argon gas or nitrogen atmosphere.
5. beta cyclo dextrin polymer preparation method according to any one of claims 1-4, it is characterised in that:The method is also Include the following steps:After second of reaction step, reaction system is cooling, filtering removes remaining alkaline chemical combination After object, obtained solid is washed with deionized, is dried in vacuo and obtains flaxen powdered samples.
6. a kind of anionic dye using described in claim 5 handle the method for methyl orange dye waste water it is characterized in that:It will Methyl orange dye adsorbent is added in the waste water solution containing methyl orange dye, so that methyl orange dye is inhaled using oscillator concussion Attached dose fully adsorbs methyl orange, is then separated by filtration, and removes the beta cyclo dextrin polymer adsorbent for having adsorbed dyestuff.
CN201810356041.2A 2018-04-19 2018-04-19 A kind of beta cyclo dextrin polymer and preparation and the method for handling anionic dye waste water using it Pending CN108579689A (en)

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CN111013553A (en) * 2019-12-26 2020-04-17 西南石油大学 Methylene blue and rhodamine B adsorbent and preparation method thereof
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CN111500110A (en) * 2020-04-28 2020-08-07 陕西大风印务科技有限公司 Transparent ink for cigarette packaging paper, coating of transparent ink and cigarette packaging paper
CN111793148A (en) * 2020-07-28 2020-10-20 福州海关技术中心 Preparation method of reusable solid-phase extraction material based on beta cyclodextrin
CN112830543A (en) * 2021-01-29 2021-05-25 湖南理工学院 Novel method for removing naphthol/naphthylamine organic matters in aqueous solution
CN113845606A (en) * 2021-09-28 2021-12-28 称意科技研发园(江苏)有限公司 Modified cyclodextrin dye adsorbent and preparation method thereof
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CN114907499A (en) * 2022-03-31 2022-08-16 中科院广州化学有限公司 Ultrahigh crosslinked beta-cyclodextrin polymer and preparation method and application thereof
CN114984928A (en) * 2022-05-19 2022-09-02 中南大学 Modified porous cyclodextrin polymer material and preparation method and application thereof

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Application publication date: 20180928