CN107398257A - A kind of preparation method and application of modified zeolite molecular sieve adsorption particle - Google Patents

A kind of preparation method and application of modified zeolite molecular sieve adsorption particle Download PDF

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CN107398257A
CN107398257A CN201710878345.0A CN201710878345A CN107398257A CN 107398257 A CN107398257 A CN 107398257A CN 201710878345 A CN201710878345 A CN 201710878345A CN 107398257 A CN107398257 A CN 107398257A
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molecular sieve
zeolite molecular
modified zeolite
chitosan
ammonia nitrogen
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郜玉楠
周历涛
孙美乔
王静
茹雅芳
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Shenyang Jianzhu University
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Shenyang Jianzhu 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
    • 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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/16Alumino-silicates
    • B01J20/18Synthetic zeolitic molecular sieves
    • B01J20/186Chemical treatments in view of modifying the properties of the sieve, e.g. increasing the stability or the activity, also decreasing the activity
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • B01J20/28016Particle form
    • 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
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The invention belongs to water-treatment technology field, and in particular to a kind of preparation method and application of modified zeolite molecular sieve adsorption particle.Technical scheme is as follows:A kind of preparation method of modified zeolite molecular sieve adsorption particle, comprises the following steps:Chitosan acetic acid colloidal sol and acetic acid zinc solution are made into first, chitosan acetic acid colloidal sol is instilled in acetic acid zinc solution and carries out complex reaction at ambient temperature, and modification of chitosan zinc solution is made;Then zeolite molecular sieve is put into sodium alginate soln and be crosslinked, the zeolite molecular sieve after crosslinking is taken out and is put into modification of chitosan zinc solution, after concussion is dried, obtain modified zeolite molecular sieve adsorption particle.The preparation method and application of modified zeolite molecular sieve adsorption particle provided by the invention, form the adsorption particle that ammonia nitrogen function is removed with low temperature, the adsorption particle can be used as filtering media application to propose mark transformation in water factory, new structures need not be increased, do not produce accessory substance, can reach cryogenic conditions go down water removal in ammonia nitrogen target.

Description

A kind of preparation method and application of modified zeolite molecular sieve adsorption particle
Technical field
The invention belongs to water-treatment technology field, and in particular to a kind of preparation method of modified zeolite molecular sieve adsorption particle And application.
Background technology
In northern China severe cold area, due to the influence of the factors such as climate, temperature, geographical position, winter source water is normal It is low to there is water quality temperature, the problem of water treatment efficiency difference;And with industrial or agricultural technology and Development of Urbanization, ammonia and nitrogen pollution is increasingly Seriously, winter raw water water temperature is relatively low in addition, and conventional water treatment process can not effectively remove ammonia nitrogen in water removal, cause effluent quality can not Meet《Standards for drinking water quality》(GB5749-2006).
At present, for the processing method of ammonia nitrogen in water, existing water factory typically uses break point chlorination, but the meeting in processing procedure The DBPs such as chloramines, chlorinatedorganic are produced, cause secondary pollution of water, while add the ill and carcinogenic of drinking person Risk.Had at normal temperatures to ammonia nitrogen using biologic pretreatment method (bio-contact oxidation and biofilter) and preferably remove effect Fruit, but change of the biological pre-treatment process to traditional handicraft is larger, it is necessary to newly-increased structures and floor space, initial investment cost It is higher, and bioactivity is influenced by environmental temperature, limits practical application of the technique in northern frore area water factory.
4A zeolite molecular sieves are a kind of alumino-silicate compounds with cubic lattice, and specific surface area is big, can be diameter For small Molecular Adsorption to inside vestibule, it is internal to have uniform microcellular structure, can be with the ion progress ion exchange in environment Without changing crystal structure, 4A zeolite molecular sieves have because of its special ion-exchange capacity and absorption property in Water purification field There is preferable application prospect.Chitosan (CTS) is a kind of natural flocculating agent, and it is widely present in shellfish, due to it Contain substantial amounts of amino and hydroxyl isoreactivity group in molecular structure, property is more active, can modify, activates and be coupled, therefore can To occur a variety of chemical modifications, and can couple to form multifunctional composite with sorbing material, coagulant, microorganism etc., There is quite wide application prospect in water process especially drinking water treatment field.
The content of the invention
The present invention provides a kind of preparation method and application of modified zeolite molecular sieve adsorption particle, and being formed, there is low temperature to remove ammonia The adsorption particle of nitrogen function, the adsorption particle can be used as filtering media application to propose mark transformation in water factory, without increasing new structures, no Produce accessory substance, can reach cryogenic conditions go down water removal in ammonia nitrogen target.
Technical scheme is as follows:
A kind of preparation method of modified zeolite molecular sieve adsorption particle, comprises the following steps:
(1) by acetum that the chitosan of deacetylation >=90% and concentration are 1%-5% according to 1:50-100 matter Amount is configured to chitosan acetic acid colloidal sol than mixing;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, wherein the quality of zinc acetate and the chitosan Than for 1:4;
(3) the chitosan acetic acid colloidal sol is instilled in the acetic acid zinc solution, stirs and evenly mixs, carry out at ambient temperature Complex reaction, reaction time 10-18h, obtain modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, being put into the complete 200-300ml concentration of dissolving is 5h is crosslinked in 1%-2% sodium alginate aqueous solutions;
(5) zeolite molecular sieve after crosslinking is taken out, is put into the modification of chitosan zinc solution, is subsequently placed in concussion In device, oscillator 120~150r/min of rotating speed, 10h is shaken under room temperature condition, form zeolite molecular sieve and modification of chitosan zinc Complex;
(6) zeolite molecular sieve and modification of chitosan Zn complex are taken out, are placed in vacuum drying chamber and dry 18h, Temperature is 60 DEG C -70 DEG C, and modified zeolite molecular sieve adsorption particle is made.
The preparation method of described modified zeolite molecular sieve adsorption particle, wherein the zeolite molecular sieve aperture is 4A.
A kind of modified zeolite molecular sieve adsorption particle goes the application of ammonia nitrogen in water removal in low temperature, comprises the following steps:Utilize Above-mentioned modified zeolite molecular sieve adsorption particle, the modified zeolite molecular sieve adsorption particle is put into containing ammonia nitrogen pollutant It is stirred in water sample, the modified zeolite molecular sieve adsorption particle dosage is 3-5g/L, mixing time 4-5h, and stirring is fast It is 4-35 DEG C to spend for 100-120r/min, range of reaction temperature, and ammonia nitrogen pollutant content is 4-6mg/L in water sample, and ammonia nitrogen is gone Except rate reaches more than 90%.
A kind of modified zeolite molecular sieve adsorption particle goes another application of ammonia nitrogen in water removal, including following step in low temperature Suddenly:Using above-mentioned modified zeolite molecular sieve adsorption particle, the modified zeolite molecular sieve adsorption particle is applied to adsorption column, Adsorption column upper strata is modified zeolite adsorption particle, particle diameter 0.2-0.3cm, adsorption particle layer height 0.5m, and adsorption column lower floor is Cobblestone supporting layer, it is highly 0.05m, filter tank average rate of filtering is 9-10m/h;Water sample containing ammonia nitrogen pollutant is entered by peristaltic pump Enter modified zeolite molecular sieve adsorption column, filter off ammonia nitrogen in water removal, ammonia nitrogen pollutant content is 4-6mg/L in water sample, ammonia nitrogen Clearance scope is 95%-99%.Wherein described adsorption column is provided with overfall and backwash water inlet, and backwashing period is 10-15d, temperature range are 4-35 DEG C.
Beneficial effects of the present invention are:
(1) modified zeolite molecular sieve adsorption particle prepared by the present invention is a kind of graininess water treatment agent, has and removes The efficiency of ammonia nitrogen in micro-polluted water, because the oxygen atom in 4A zeolite molecular sieve skeletons is common to two neighboring tetrahedron, this Kind structure can accommodate cation, and so as to carry out cation exchange reaction, therefore 4A zeolite molecular sieves have higher choosing to ammonia nitrogen Choose friends transsexual.By the way that modification of chitosan and 4A zeolite molecular sieves are crosslinked, chitosan surface amino groups, hydroxyl isoreactivity are utilized The chelatropic reaction that group occurs with metal ion, makes metal ion d orbital slots, is improved by the effect of coordinate bond to ammonia in water The adsorption capacity of nitrogen small molecule, so as to strengthen removal efficiency of the 4A zeolite molecular sieves to ammonia nitrogen.
(2) cost of investment of the present invention is low, cold operation effect is good, the regeneration period is long, recoverable, constructs without newly-increased Thing, transformed suitable for Large Water Works filtering technique section, and the application of small-scale integration apparatus.
Brief description of the drawings
Fig. 1 is the modified zeolite molecular sieve adsorption particle scanning electron microscopic picture prepared in embodiment 1;
Fig. 2 is the adsorption column installation drawing using modified zeolite molecular sieve adsorption particle as filtrate;
Wherein:1:Water tank;2:Peristaltic pump;3:Flowmeter;4:Water inlet;5:Modified zeolite molecular sieve adsorption particle filtrate;6: Cobblestone supporting layer;7:Water outlet;8:Backwash water inlet;
Fig. 3 is modified zeolite molecular sieve curve of adsorption kinetics;
Fig. 4 is modified zeolite molecular sieve pseudo-first-order kinetic curve;
Fig. 5 is modified zeolite molecular sieve pseudo-second order kinetic curve;
Fig. 6 is modified zeolite molecular sieve adsorption isotherm model analysis;
Fig. 7 is the lnK of modified zeolite molecular sieve absorption ammonia nitrogendWith 1/T graphs of a relation.
Embodiment
Following specific embodiments are the further explanations to present invention, but the substantive content of the present invention is not limited in Described in following specific embodiments, any combination between any specific embodiment and this hair is belonged to the simple change of preparation process Bright required protection domain.
Embodiment 1
The preparation method of the modified zeolite molecular sieve adsorption particle of the present embodiment follows the steps below:
(1) by acetum that the chitosan of deacetylation 90% and concentration are 2% according to 1:50 mass ratio mixing, matches somebody with somebody Chitosan acetic acid colloidal sol is made;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, wherein zinc acetate is molten with preparing chitosan acetic acid The mass ratio of chitosan used is 1 during glue:4;
(3) chitosan acetic acid colloidal sol obtained by step (1) is instilled in acetic acid zinc solution, stirred and evenly mixed, at ambient temperature Complex reaction is carried out, reaction time 10h, obtains modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, it is 1% marine alga to be put into the complete 200ml concentration of dissolving 5h is crosslinked in acid sodium aqueous solution;
(5) zeolite molecular sieve after crosslinking is taken out and be put into modification of chitosan zinc solution obtained by step (3), then put The rotating speed 120r/min in oscillator, 10h is shaken under room temperature condition, form the cooperation of zeolite molecular sieve and modification of chitosan zinc Thing;
(6) gained zeolite molecular sieve in step (5) is taken out with modification of chitosan Zn complex, is placed in vacuum drying chamber 18h is dried in (60 DEG C), modified zeolite molecular sieve adsorption particle is made.
Wherein, described zeolite molecules mesh size is 4A.
Prepared modified zeolite molecular sieve adsorption particle is observed using ESEM, as shown in figure 1, particle table Face is without sclay texture, and rough surface out-of-flatness, and more protruding features are presented.
The modified zeolite molecular sieve adsorption particle of the present embodiment removes the application of ammonia nitrogen in low temperature water, as shown in Fig. 2 according to Following steps are carried out:
The modified zeolite molecular sieve adsorption particle of embodiment is applied to adsorption column, adsorption column upper strata is adsorbed for modified zeolite Particle 5, particle diameter 0.2-0.3cm, adsorption particle layer height 0.5m, lower floor are cobblestone supporting layer 6, are highly 0.05m, filter tank Average rate of filtering is 9.5m/h;Raw water containing ammonia nitrogen pollutant enters modified zeolite molecular sieve adsorption column by peristaltic pump 2, filters off Ammonia nitrogen in water removal, the clearance scope of ammonia nitrogen is 95%-99%;Wherein, described adsorption column is provided with overfall and backwash Water inlet 8, backwashing period 15d.
The described range of reaction temperature for removing ammonia nitrogen in water removal is 4-5 DEG C.
Ammonia nitrogen pollutant concentration range is 4-6mg/L in described raw water.
Embodiment 2
The preparation method of the modified zeolite molecular sieve adsorption particle of the present embodiment follows the steps below:
(1) by acetum that the chitosan of deacetylation 95% and concentration are 5% according to 1:100 mass ratio mixing, It is configured to chitosan acetic acid colloidal sol;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, wherein zinc acetate is molten with preparing chitosan acetic acid The mass ratio of chitosan used is 1 during glue:4;
(3) chitosan acetic acid colloidal sol obtained by step (1) is instilled in acetic acid zinc solution, stirred and evenly mixed, at ambient temperature Complex reaction is carried out, reaction time 18h, obtains modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, it is 2% marine alga to be put into the complete 300ml concentration of dissolving 5h is crosslinked in acid sodium aqueous solution;
(5) zeolite molecular sieve after crosslinking is taken out and be put into modification of chitosan zinc solution obtained by step (3), then put The rotating speed 150r/min in oscillator, 10h is shaken under room temperature condition, form the cooperation of zeolite molecular sieve and modification of chitosan zinc Thing;
(6) gained zeolite molecular sieve in step (5) is taken out with modification of chitosan Zn complex, is placed in vacuum drying chamber 18h is dried in (70 DEG C), modified zeolite molecular sieve adsorption particle is made.
Wherein, described zeolite molecules mesh size is 4A.
The adsorption dynamics adsorption kinetics research of the modified zeolite molecular sieve adsorption particle of the present embodiment, as shown in Fig. 3, Fig. 4, Fig. 5, is pressed Carried out according to following steps:
By modified zeolite molecular sieve adsorption particle 1.0g be placed in 100mL mass concentrations scope for 4~5mg/L ammonia nitrogen solutions in In ground conical flask, conical flask is placed in gas bath constant temperature oscillator, (10 DEG C) vibrations under 200r/min, cryogenic conditions, respectively Sample is taken out in 15,30,60,120,180,240,300,360,420,480,540,600,660 and 720min, filtered 0.45um miillpore filters, ammonia nitrogen concentration is determined using Nessler's reagent photometer.
The curve of adsorption kinetics of modified zeolite molecular sieve adsorption particle is modified as shown in figure 3, before starting the reaction in 1h The rate of adsorption of zeolite molecular sieve adsorption particle is fast, and linear absorption, adsorbance reaches 0.214mg/g, with the reaction time Carry out, the rate of adsorption is gradually slack-off, and adsorbance slowly rises;When reaction proceeds to 12h, adsorption equilibrium, modified zeolite are reached The equilibrium adsorption capacity 0.286mg/g of molecular sieve adsorption particle.
In order to accurately react the ammonia nitrogen concentration trend that (10 DEG C) change over time under cryogenic and disclose its suction Attached process, modified zeolite molecular sieve adsorption particle is carried out using Lagergren pseudo-first-orders and quasi- second- order reaction kinetics model The fitting of test data,
Lagergren pseudo-first-order kinetics equations:
Lagergren pseudo-second order kinetic equations:
By modified zeolite molecular sieve adsorption particle (10 DEG C) adsorption dynamics adsorption kinetics data under cryogenic, to 1/qtWith 1/t Relation and t/qtLinear fit (as shown in Figure 4 and Figure 5) is carried out with t relation, can be distinguished by the slope and intercept of straight line Try to achieve parameter qe1、k1、qe2、k2, the results are shown in Table 1.
The kinetic parameter of table 1
Pass through the linearly dependent coefficient R to fitting2It is compared and understands, the linearly dependent coefficient of pseudo-second order kinetic fitting (R2=0.999) it is higher than pseudo-first-order dynamics (R2=0.979), it can thus be concluded that, the process of modified zeolite molecular sieve absorption ammonia nitrogen is more Meet pseudo-second order kinetic model.The equilibrium adsorption capacity being calculated by pseudo-first-order kinetics equation is respectively 0.317mg/g, With result of the test obtained by modified zeolite molecular sieve adsorption particle (10 DEG C) under cryogenic equilibrium adsorption capacity 0.286mg/g phases Difference is larger, and the data (0.299mg/g) and test value the data obtained of pseudo-second order kinetic equation model are very close.
Embodiment 3
The preparation method of the modified zeolite molecular sieve adsorption particle of the present embodiment follows the steps below:
(1) by acetum that the chitosan of deacetylation 90% and concentration are 3% according to 1:100 mass ratio mixing, It is configured to chitosan acetic acid colloidal sol;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, wherein zinc acetate is molten with preparing chitosan acetic acid The mass ratio of chitosan used is 1 during glue:4;
(3) chitosan acetic acid colloidal sol obtained by step (1) is instilled in acetic acid zinc solution, stirred and evenly mixed, at ambient temperature Complex reaction is carried out, reaction time 18h, obtains modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, it is 1% marine alga to be put into the complete 300ml concentration of dissolving 5h is crosslinked in acid sodium aqueous solution;
(5) zeolite molecular sieve after crosslinking is taken out and be put into modification of chitosan zinc solution obtained by step (3), then put The rotating speed 150r/min in oscillator, 10h is shaken under room temperature condition, form the cooperation of zeolite molecular sieve and modification of chitosan zinc Thing;
(6) gained zeolite molecular sieve in step (5) is taken out with modification of chitosan Zn complex, is placed in vacuum drying chamber 18h is dried in (70 DEG C), modified zeolite molecular sieve adsorption particle is made.
Wherein, described zeolite molecules mesh size is 4A.
The adsorption isotherm research of the modified zeolite of the present embodiment, as shown in fig. 6, following the steps below:
By modified zeolite molecular sieve adsorption particle 1.0g be placed in 100mL mass concentrations for 2,4,6,8,10,12mg/L ammonia nitrogens Solution is placed in gas bath constant temperature oscillator in ground conical flask, by conical flask, (10 DEG C) vibrations under 200r/min, cryogenic conditions After 12h adsorption equilibriums, 0.45um miillpore filters, measure filtrate ammonia nitrogen concentration C are filteredeCalculate modified zeolite molecular sieve equilibrium adsorption Amount.
According to modified zeolite molecular sieve adsorption particle under cryogenic (10 DEG C), the vibration adsorption test number to ammonia nitrogen According to, Langmuir and Freundlich isotherm adsorption models are respectively adopted and are fitted (Fig. 6), obtained respectively by Fig. 6 needed for Parameter qm、KL、KFWith 1/n numerical value, 2 are the results are shown in Table.
Langmuir isothermal adsorpting equation formulas:
Freundlich isothermal adsorpting equation formulas:
The thermoisopleth parameter of table 2
From Fig. 6 and table 2, the absorption of (10 DEG C) to ammonia nitrogen etc. under cryogenic of modified zeolite molecular sieve adsorption particle The result of warm line fitting shows, the multiple correlation coefficient (R of Langmuir adsorption isotherm line models2=0.999) it is higher than Multiple correlation coefficient (the R of Freundlich adsorption isotherm line models2=0.989) Langmuir adsorption isotherm line model energy, is illustrated More accurately description modified zeolite molecular sieve adsorbs the characteristic of ammonia nitrogen.1/n is different in Freundlich adsorption isotherm equations Matter coefficient, generally, when 1/n is more than 2, illustrate that absorption is more difficult;When 1/n is equal to 1, linear adsorption is represented;1/n is more than 0.1 During less than 0.5, easily absorption is represented.The heterogeneous coefficient (1/n=0.499) of modified zeolite molecular sieve in this research, illustrate to be modified The process of zeolite molecular sieve absorption ammonia nitrogen is easily carried out.According to Langmuir adsorption isotherm equations, the modified boiling being calculated (10 DEG C) are 0.817mg/g to the monolayer maximal absorptive capacity of ammonia nitrogen in raw water under stone molecular sieve adsorption particle cryogenic conditions.
Embodiment 4
The preparation method of the modified zeolite molecular sieve adsorption particle of the present embodiment follows the steps below:
(1) by acetum that the chitosan of deacetylation 95% and concentration are 1% according to 1:70 mass ratio mixing, matches somebody with somebody Chitosan acetic acid colloidal sol is made;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, wherein zinc acetate is molten with preparing chitosan acetic acid The mass ratio of chitosan used is 1 during glue:4;
(3) chitosan acetic acid colloidal sol obtained by step (1) is instilled in acetic acid zinc solution, stirred and evenly mixed, at ambient temperature Complex reaction is carried out, reaction time 15h, obtains modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, it is 2% marine alga to be put into the complete 200ml concentration of dissolving 5h is crosslinked in acid sodium aqueous solution;
(5) zeolite molecular sieve after crosslinking is taken out and be put into modification of chitosan zinc solution obtained by step (3), then put The rotating speed 120r/min in oscillator, 10h is shaken under room temperature condition, form the cooperation of zeolite molecular sieve and modification of chitosan zinc Thing;
(6) gained zeolite molecular sieve in step (5) is taken out with modification of chitosan Zn complex, is placed in vacuum drying chamber 18h is dried in (70 DEG C), modified zeolite molecular sieve adsorption particle is made.
Wherein, described zeolite molecules mesh size is 4A.
The Adsorption thermodynamics research of the modified zeolite of the present embodiment, as shown in fig. 7, following the steps below:
Modified zeolite molecular sieve 1.0g is placed in 100mL mass concentrations scope in 4~5mg/L ammonia nitrogen solutions, to incite somebody to action respectively Conical flask is placed in gas bath constant temperature oscillator, and respectively in 200r/min, temperature is shaken under the conditions of being 5 DEG C, 10 DEG C, 15 DEG C, 25 DEG C, 35 DEG C After swinging 12h adsorption equilibriums, 0.45um miillpore filters are filtered, determine filtrate ammonia nitrogen concentration.
To calculate the thermodynamic parameter that modified zeolite molecular sieve adsorbs ammonia nitrogen, under experiment investigation different temperatures (5 DEG C, 10 DEG C, 15 DEG C, 25 DEG C, 35 DEG C) adsorption equilibrium state.Gibbs free (Δ G), enthalpy (Δ H), entropy (Δ S) pass through below equation Calculate:
Δ G=-RTlnKd (7)
According to modified zeolite molecular sieve ammonia nitrogen during (5 DEG C, 10 DEG C, 15 DEG C, 25 DEG C, 35 DEG C) are to water under condition of different temperatures Desorption balance data, the K under condition of different temperatures is calculated by formula (6)d, then corresponding temperature calculated by formula (7) Jeep this free energy Δ G under the conditions of degree, finally by formula (8) to lnKdLinear fit is carried out (such as Fig. 7 institutes with 1/T relations Show), enthalpy change (Δ H) corresponding to adsorption reaction and Entropy Changes (Δ S) can be calculated respectively by the slope and intercept of straight line, the results are shown in Table 3。
The adsorption thermodynamic parameters of table 3
From Fig. 7 and table 3, the enthalpy change Δ H of modified zeolite molecular sieve absorption ammonia nitrogen is on the occasion of illustrating modified zeolite molecule The absorption sieved to ammonia nitrogen is the endothermic reaction, while the ability for illustrating to adsorb ammonia nitrogen increases with the rise of temperature.Temperature Rise is advantageous to adsorption reaction progress, this free energy of (5 DEG C, 10 DEG C, 15 DEG C, 25 DEG C, 35 DEG C) jeep under condition of different temperatures Become Δ G<0 is negative value, and with the rise of temperature, Δ G is less and less, and it is spontaneous process to show the adsorption process, simultaneously Spontaneous degree is increasing with the rise of temperature.Entropy Changes Δ S>0 is on the occasion of showing absorption of the modified zeolite molecular sieve to ammonia nitrogen Increase for entropy and react, and illustrate that avtive spot, the free degree of adsorbate and confusion degree all increase with the rise of temperature.

Claims (5)

1. a kind of preparation method of modified zeolite molecular sieve adsorption particle, it is characterised in that comprise the following steps:
(1) by acetum that the chitosan of deacetylation >=90% and concentration are 1%-5% according to 1:50-100 mass ratio Mixing, is configured to chitosan acetic acid colloidal sol;
(2) zinc acetate is dissolved in deionized water and acetic acid zinc solution is made, the mass ratio of wherein zinc acetate and the chitosan is 1:4;
(3) the chitosan acetic acid colloidal sol is instilled in the acetic acid zinc solution, stirs and evenly mixs, be complexed at ambient temperature Reaction, reaction time 10-18h, obtains modification of chitosan zinc solution;
(4) 50g zeolite molecular sieves are rinsed well with deionized water, it is 1%-2% to be put into the complete 200-300ml concentration of dissolving 5h is crosslinked in sodium alginate aqueous solution;
(5) zeolite molecular sieve after crosslinking is taken out, is put into the modification of chitosan zinc solution, is subsequently placed in oscillator In, oscillator 120~150r/min of rotating speed, 10h is shaken under room temperature condition, form matching somebody with somebody for zeolite molecular sieve and modification of chitosan zinc Compound;
(6) zeolite molecular sieve and modification of chitosan Zn complex are taken out, is placed in vacuum drying chamber and dries 18h, temperature For 60 DEG C -70 DEG C, modified zeolite molecular sieve adsorption particle is made.
2. the preparation method of modified zeolite molecular sieve adsorption particle according to claim 1, it is characterised in that the zeolite Molecular sieve bore diameter is 4A.
3. a kind of modified zeolite molecular sieve adsorption particle goes the application of ammonia nitrogen in water removal in low temperature, it is characterised in that including as follows Step:Using modified zeolite molecular sieve adsorption particle as claimed in claim 1 or 2, the modified zeolite molecular sieve is adsorbed Particle is put into the water sample containing ammonia nitrogen pollutant and is stirred, and the modified zeolite molecular sieve adsorption particle dosage is 3- 5g/L, mixing time 4-5h, mixing speed 100-120r/min, range of reaction temperature are 4-35 DEG C, and ammonia nitrogen is dirty in water sample It is 4-6mg/L to contaminate thing content, and the clearance of ammonia nitrogen reaches more than 90%.
4. a kind of modified zeolite molecular sieve adsorption particle goes the application of ammonia nitrogen in water removal in low temperature, it is characterised in that including as follows Step:Using modified zeolite molecular sieve adsorption particle as claimed in claim 1 or 2, the modified zeolite molecular sieve is adsorbed Particle is applied to adsorption column, and adsorption column upper strata is modified zeolite adsorption particle, particle diameter 0.2-0.3cm, adsorption particle layer height 0.5m, adsorption column lower floor are cobblestone supporting layer, are highly 0.05m, and filter tank average rate of filtering is 9-10m/h;Containing ammonia nitrogen pollutant Water sample modified zeolite molecular sieve adsorption column is entered by peristaltic pump, filter off ammonia nitrogen in water removal, ammonia nitrogen pollutant contains in water sample Measure as 4-6mg/L, the clearance scope of ammonia nitrogen is 95%-99%.
5. modified zeolite molecular sieve adsorption particle according to claim 4 goes the application of ammonia nitrogen in water removal in low temperature, it is special Sign is that the adsorption column is provided with overfall and backwash water inlet, backwashing period 10-15d, temperature range 4-35 ℃。
CN201710878345.0A 2017-09-26 2017-09-26 A kind of preparation method and application of modified zeolite molecular sieve adsorption particle Pending CN107398257A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108940219A (en) * 2018-07-12 2018-12-07 浙江正洁环境科技有限公司 A kind of anti-acid heavy metal absorbent and preparation method thereof
CN112707475A (en) * 2019-10-25 2021-04-27 宁波方太厨具有限公司 Adsorption powder, conductive polar plate, filter membrane and roll type filter element
CN113976074A (en) * 2021-11-23 2022-01-28 沈阳建筑大学 Iron-manganese mud composite gel ball adsorption antimony removal material and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101347720A (en) * 2008-09-04 2009-01-21 华南师范大学 Method for preparing chitosan porous microsphere sorbent by metal ion imprinting and crosslinking methods as well as use
CN105084384A (en) * 2015-09-01 2015-11-25 佛山蓝途科技有限公司 Loofah sponge zeolite molecular sieve for water muddy matter adsorption separation and preparation method of loofah sponge zeolite molecular sieve
CN106669621A (en) * 2017-01-18 2017-05-17 沈阳建筑大学 Preparation method and application of chitosan/zeolite molecular sieve adsorbent
CN106745610A (en) * 2016-12-29 2017-05-31 沈阳建筑大学 Modification of chitosan carries the preparation of Zn complex and the application of removal ammonia nitrogen pollutant

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101347720A (en) * 2008-09-04 2009-01-21 华南师范大学 Method for preparing chitosan porous microsphere sorbent by metal ion imprinting and crosslinking methods as well as use
CN105084384A (en) * 2015-09-01 2015-11-25 佛山蓝途科技有限公司 Loofah sponge zeolite molecular sieve for water muddy matter adsorption separation and preparation method of loofah sponge zeolite molecular sieve
CN106745610A (en) * 2016-12-29 2017-05-31 沈阳建筑大学 Modification of chitosan carries the preparation of Zn complex and the application of removal ammonia nitrogen pollutant
CN106669621A (en) * 2017-01-18 2017-05-17 沈阳建筑大学 Preparation method and application of chitosan/zeolite molecular sieve adsorbent

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
孙美乔等: "改性壳聚糖强化混凝处理低温氨氮污染水源水研究", 《给水排水》 *
郎惠云等: "壳聚糖_Zn(Ⅱ)配合物对尿素的吸附行为的研究", 《食品科学》 *
郭祎阁等: "壳聚糖包覆介孔微孔分子筛去除水中的氨氮", 《环境工程学报》 *
顾其胜等: "《海藻酸盐基生物医用材料与临床医学》", 30 April 2015 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108940219A (en) * 2018-07-12 2018-12-07 浙江正洁环境科技有限公司 A kind of anti-acid heavy metal absorbent and preparation method thereof
CN112707475A (en) * 2019-10-25 2021-04-27 宁波方太厨具有限公司 Adsorption powder, conductive polar plate, filter membrane and roll type filter element
CN112707475B (en) * 2019-10-25 2022-11-01 宁波方太厨具有限公司 Adsorption powder, conductive polar plate, filter membrane and roll type filter element
CN113976074A (en) * 2021-11-23 2022-01-28 沈阳建筑大学 Iron-manganese mud composite gel ball adsorption antimony removal material and preparation method thereof

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