CN109759018A - The preparation method and application of support type Manganese Ferrite adsorbent - Google Patents

The preparation method and application of support type Manganese Ferrite adsorbent Download PDF

Info

Publication number
CN109759018A
CN109759018A CN201910218395.5A CN201910218395A CN109759018A CN 109759018 A CN109759018 A CN 109759018A CN 201910218395 A CN201910218395 A CN 201910218395A CN 109759018 A CN109759018 A CN 109759018A
Authority
CN
China
Prior art keywords
manganese ferrite
support type
type manganese
adsorbent
ferrite adsorbent
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.)
Pending
Application number
CN201910218395.5A
Other languages
Chinese (zh)
Inventor
周耀渝
陈禹欣
李培培
吴世康
杨�远
罗琳
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.)
Hunan Agricultural University
Original Assignee
Hunan Agricultural University
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 Hunan Agricultural University filed Critical Hunan Agricultural University
Priority to CN201910218395.5A priority Critical patent/CN109759018A/en
Publication of CN109759018A publication Critical patent/CN109759018A/en
Pending legal-status Critical Current

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The present invention relates to environment protection fields, disclose a kind of preparation method and application of support type Manganese Ferrite adsorbent.The preparation method of support type Manganese Ferrite adsorbent includes: that (1) mixes vinasse with containing manganous salt and trivalent iron salt mixed liquor, mixed condition makes manganous salt and trivalent iron salt form Manganese Ferrite, and be carried on the vinasse, obtain support type Manganese Ferrite adsorbent precursors;(2) after the support type Manganese Ferrite adsorbent precursors drying and roasting, support type Manganese Ferrite adsorbent is obtained.The adsorbent has the advantages that excellent in magnetic characteristics, large specific surface area, surface-active site is high, chemical stability is good, while big to the adsorption efficiency of atoxylic acid height, adsorption capacity.

Description

The preparation method and application of support type Manganese Ferrite adsorbent
Technical field
The present invention relates to environment protection fields, and in particular to a kind of preparation method and application of support type Manganese Ferrite adsorbent.
Background technique
For a long time, the arsenic in water body is always focus concerned by people to the harm of human health.Studies have shown that when long Between drink the generation that the water containing low arsenic concentration also results in many diseases, therefore the minimizing technology of arsenic is always environmental area in water The heat subject of research.Currently, the method for removal Pollutants in Wastewater mainly has: chemical precipitation or flocculence, membrane technology, electrolysis Reduction, catalytic degradation, ion exchange and absorption method, wherein absorption method is because of its easy to operate, the wide variety of adsorbent, operation week The advantages such as the phase is short, treatment effeciency is high and be widely used.
In numerous arsenicals, atoxylic acid is a kind of novel organoarsenium compound, is widely used in moving The additive of object feed.However in recent years the study found that organoarsenium compound only has minimum a part could in animal body It is metabolized or absorbs, rest part can be drained intactly in the form of excrement and urine, and wherein arsenic content is more than 40mg/ Kg, these water-soluble atoxylic acid are degraded to high poison by biology and abiotic approach in 30 days after excrement is drained Property inorganic arsenic, causes soil and groundwater arsenic pollution serious, influences human health.Therefore, the p-aminophenyl in aqueous solution is removed Arsenic acid also becomes the hot spot studied both at home and abroad.
Summary of the invention
The purpose of the invention is to overcome atoxylic acid in animal feed of the existing technology to cause water body dirty The problem of dye, a kind of support type Manganese Ferrite adsorbent and preparation method thereof is provided, which has excellent in magnetic characteristics, specific surface The advantage that product is big, surface-active site is high, chemical stability is good, while, absorption high to the adsorption efficiency of atoxylic acid is held Amount is big.
To achieve the goals above, first aspect present invention provides a kind of preparation method of support type Manganese Ferrite adsorbent, This method comprises:
(1) vinasse are mixed in containing manganous salt and trivalent iron salt mixed liquor, mixed condition makes divalent Manganese salt and trivalent iron salt form Manganese Ferrite, and are carried on the vinasse, obtain support type Manganese Ferrite adsorbent precursors;
(2) after the support type Manganese Ferrite adsorbent precursors drying and roasting, support type Manganese Ferrite adsorbent is obtained.
Preferably, the condition of mixing described in step (1) include: pH be 9-11, temperature is 50-70 DEG C, time 3-5h.
Preferably, the trivalent iron salt based on 100 parts by weight in step (1), the dosage of the vinasse are 30-90 parts by weight, The dosage of the manganous salt is 15-70 parts by weight.
Preferably, manganous salt described in step (1) is selected from manganese sulfate and/or manganese chloride, and the trivalent iron salt is selected from chlorine Change at least one of iron, ferric sulfate and ferric nitrate.
It preferably, further include that the support type Manganese Ferrite adsorbent precursors are washed before the drying in step (2) It washs.
Preferably, temperature dry described in step (2) be 90-110 DEG C, time 20-30h, the condition of the roasting Include: in an inert atmosphere, temperature be 600-800 DEG C, time 0.5-2h.
Preferably, this method further includes being ground, being washed to the support type Manganese Ferrite adsorbent, dried, and is obtained most Finished product.
Preferably, it is described grinding include the support type Manganese Ferrite adsorbent is ground to granularity be 100 mesh more than, it is described The condition of washing includes using milli-Q water to the pH of cleaning solution for 6.5-7.0, and the temperature of the drying is 90-110 DEG C.
Second aspect of the present invention provides the support type Manganese Ferrite adsorbent prepared by the above method.
Third aspect present invention provides the support type Manganese Ferrite adsorbent prepared by the above method in removing p-aminophenyl arsine Application in acid.
Through the above technical solutions, the invention has the following advantages that
1, support type Manganese Ferrite adsorbent of the invention utilizes manganous salt and ferric iron using vinasse as adsorbing agent carrier Salt synthesis Manganese Ferrite is simultaneously carried on carrier, forms support type Manganese Ferrite adsorbent precursors, so that vinasse conversion is made a living by roasting Object charcoal makes adsorbent have loose porous structure together so that charcoal and Manganese Ferrite preferably load;
2, support type Manganese Ferrite adsorbent of the invention has excellent magnetic characteristic, therefore can be by outer after the completion of absorption Portion's magnetic fields realize the quick separating with liquid phase, avoid centrifugation or are separated by filtration bring inconvenience, facilitate recycling, drop Low operation difficulty and cost, improve adsorption efficiency;
3, support type Manganese Ferrite adsorbent of the invention has more loose porous structure, apparent distribution of particles, height Specific surface area has certain water solubility and dispersibility, provides more active site, has to atoxylic acid good Absorption property;
4, support type Manganese Ferrite adsorbent preparation process of the invention is simple, low in cost, is suitable for large-scale production and answers With;
5, support type Manganese Ferrite adsorbent of the invention is adsorbable and removes the atoxylic acid in water body, and adsorbs effect Rate is high, and condition is easy to control, and chemical property is stablized, and can be widely used in the water body containing atoxylic acid.
Detailed description of the invention
Fig. 1 is the scanning electron microscope diagram of support type Manganese Ferrite adsorbent of the invention;
Fig. 2 is the transmission electron microscope picture of support type Manganese Ferrite adsorbent of the invention;
Fig. 3 is the pass that support type Manganese Ferrite adsorbent of the invention changes the adsorption efficiency of atoxylic acid with pH value It is schematic diagram;
Fig. 4 is the pass that support type Manganese Ferrite adsorbent of the invention varies with temperature the adsorption efficiency of atoxylic acid It is schematic diagram;
Fig. 5 is that support type Manganese Ferrite adsorbent of the invention changes the adsorption efficiency of atoxylic acid with adsorption time Relation schematic diagram;
Fig. 6 be support type Manganese Ferrite adsorbent of the invention to the adsorption efficiency of atoxylic acid with atoxylic acid The relation schematic diagram of initial concentration variation;
Fig. 7 is that support type Manganese Ferrite adsorbent of the invention becomes the adsorption efficiency of atoxylic acid with adsorbent amount The relation schematic diagram of change.
Specific embodiment
The endpoint of disclosed range and any value are not limited to the accurate range or value herein, these ranges or Value should be understood as comprising the value close to these ranges or value.For numberical range, between the endpoint value of each range, respectively It can be combined with each other between the endpoint value of a range and individual point value, and individually between point value and obtain one or more New numberical range, these numberical ranges should be considered as specific open herein.
In a first aspect, the present invention a kind of preparation method of support type Manganese Ferrite adsorbent is provided this method comprises:
(1) vinasse are mixed in containing manganous salt and trivalent iron salt mixed liquor, mixed condition makes divalent Manganese salt and trivalent iron salt form Manganese Ferrite, and are carried on the vinasse carrier, obtain support type Manganese Ferrite adsorbent precursors;
(2) after the support type Manganese Ferrite adsorbent precursors drying and roasting, support type Manganese Ferrite adsorbent is obtained.
Preferably, the condition of mixing described in step (1) include: pH be 9-11, temperature is 50-70 DEG C, time 3-5h.
In the present invention, vinasse refer to remaining residue after the wine brewing such as rice, wheat, jowar.In order to be more conducive to described The mixed process of absorption on vinasse carrier, vinasse and manganous salt and trivalent iron salt is preferred are as follows: vinasse mixed with ultrapure water, Under the conditions of 22-28 DEG C, 20-35min is stirred, manganous salt and trivalent iron salt are then added to the complete spent wash of mixing In, strong base solution is added after the solid is completely dissolved and adjusts pH value to 9-11, obtained mixture is put into thermostatic drying chamber In reacted, wherein the strong base solution is preferably the sodium hydroxide solution of 5mol/L, be more advantageous to the formation of Manganese Ferrite with Load.
Preferably, the trivalent iron salt based on 100 parts by weight in step (1), the dosage of the vinasse are 30-90 parts by weight, It is specifically as follows 30 parts by weight, 40 parts by weight, 50 parts by weight, 60 parts by weight, 70 parts by weight, 80 parts by weight, 90 parts by weight, and Any two in these point values constitute in the range of arbitrary value, the dosage of the manganous salt is 15-70 parts by weight, tool Body can for 15 parts by weight, 25 parts by weight, 35 parts by weight, 45 parts by weight, 55 parts by weight, 65 parts by weight, 70 parts by weight and this Arbitrary value in the range of any two in point values are constituted a bit.
Preferably, manganous salt described in step (1) is selected from manganese sulfate and/or manganese chloride, and the trivalent iron salt is selected from chlorine Change at least one of iron, ferric sulfate and ferric nitrate.
It preferably, further include that the support type Manganese Ferrite adsorbent precursors are washed before the drying in step (2) It washs, washing preferably filter after repeatedly washing using ultrapure water.
Preferably, temperature dry described in step (2) is 90-110 DEG C, be specifically as follows 90 DEG C, 95 DEG C, 100 DEG C, Any two in 105 DEG C, 110 DEG C and these point values constitute in the range of arbitrary value, time 20-30h, specifically Can any two for 20h, 22h, for 24 hours, in 26h, 28h, 30h and these point values constitute in the range of arbitrary value. The condition of the roasting include: in an inert atmosphere, temperature be 600-800 DEG C, be specifically as follows 600 DEG C, 650 DEG C, 700 DEG C, 750 DEG C, any two in 800 DEG C and these point values constitute in the range of arbitrary value, calcining time 0.5- 2h, the arbitrary value being specifically as follows in the range of any two in 0.5h, 1h, 1.5h, 2h and these point values are constituted. Wherein, the inert gas is preferably nitrogen.Material is preferably placed in quartz boat by roasting process, is put into heating rate 5 DEG C/tube furnace of min in calcined.
In the present invention, vinasse are carried out being mixed to form support type ferrous acid in containing manganous salt and trivalent iron salt mixed liquor Manganese adsorbent precursors, then after drying and roasting, obtain support type Manganese Ferrite adsorbent.But the present inventor is grinding It finds during studying carefully, after to the support type Manganese Ferrite adsorbent by further grinding, washing, is dry, can be made More excellent performance of adsorbent final products.
The grinding, washing, drying process of the support type Manganese Ferrite adsorbent are not particularly limited in the present invention, Such as can preferably, the grinding includes that the support type Manganese Ferrite adsorbent is ground to granularity using agate mortar to be More than 100 mesh, the condition of the washing includes using milli-Q water to the pH of cleaning solution for 6.5-7.0, the temperature of the drying Degree is 90-110 DEG C.
Second aspect, the present invention provides the support type Manganese Ferrite adsorbents prepared by the above method.
The third aspect, the present invention provides the support type Manganese Ferrite adsorbents prepared by the above method in removing p-aminophenyl Application in arsenic acid.
The present invention will be described in detail by way of examples below.In following embodiment, electron microscope scanning is used Scanning electron microscope, model QUANTA250FEG;Transmission electron microscope analysis uses transmission electron microscope, model Tecnal G220;The concentration mensuration of atoxylic acid solution uses ultraviolet-uisible spectrophotometer, model UV1900;Vinasse come from wine Gui Jiu limited liability company;Atoxylic acid is purchased from Ti Xiai chemical conversion industry Development Co., Ltd, specification GR;Other chemistry Product are commercially available product.
Embodiment 1
(1) 5g vinasse are weighed to mix with 100mL ultrapure water, 30min is stirred under the conditions of 25 DEG C, makes vinasse substantially uniformity It is dispersed in water, then by 5.5g MnSO4·4H2O and 8g Fe2(SO4)3It is added in spent wash, after the solid is completely dissolved The pH value of mixed liquor is adjusted to 10 with the NaOH solution of 5mol/L, mixed liquor is put into 60 DEG C of drying boxes and reacts 4h;
(2) it by the sediment generated in mixed liquor (support type Manganese Ferrite adsorbent precursors) after being separated in mixed liquor, uses Ultrapure water is cleaned multiple times, is filtered, and is dried at 100 DEG C for 24 hours, in N2It under environment, puts the precipitate in quartz boat, is put into With 700 DEG C of calcining 1h in the tube furnace of 5 DEG C/min of heating rate, it is fully crystallized metal;
(3) in N2It after being cooled to room temperature step (2) products therefrom under environment, is ground using agate mortar, crosses 100 mesh Sieve is repeatedly washed until the pH of cleaning solution reaches 6.5 with ultrapure water, product is dried at 100 DEG C, obtains support type Manganese Ferrite Adsorbent.
Electron microscope observation is scanned to support type Manganese Ferrite adsorbent made from embodiment 1, as shown in Figure 1, iron Together with manganese oxysome is preferably loaded with charcoal, charcoal loads Manganese Ferrite and has more loose porous structure, it will be apparent that Distribution of particles has good absorption property.Transmission electron microscope point is carried out to support type Manganese Ferrite adsorbent made from embodiment 1 Analysis has certain water solubility and dispersion as shown in Fig. 2, the material dispersion effect of charcoal obtained load ferrimanganic oxysome is preferable Property, more active site, this structure and its excellent magnetic characteristic are provided, its adsorption effect is advantageously implemented.
Embodiment 2
(1) 5g vinasse are weighed to mix with 100mL ultrapure water, 30min is stirred under the conditions of 25 DEG C, makes vinasse substantially uniformity It is dispersed in water, then by 2.58g MnSO4·H2O and 14.8g FeCl3·6H2O is added in spent wash, to solid whole The pH value of mixed liquor is adjusted to 9 with the NaOH solution of 5mol/L after dissolution, mixed liquor is put into 50 DEG C of drying boxes and reacts 5h;
(2) it by the sediment generated in mixed liquor (support type Manganese Ferrite adsorbent precursors) after being separated in mixed liquor, uses Ultrapure water is cleaned multiple times, is filtered, the dry 30h at 90 DEG C, in N2It under environment, puts the precipitate in quartz boat, is put into With 600 DEG C of calcining 2h in the tube furnace of 5 DEG C/min of heating rate, it is fully crystallized metal;
(3) in N2It after being cooled to room temperature step (2) products therefrom under environment, is ground using agate mortar, crosses 100 mesh Sieve is repeatedly washed until the pH of cleaning solution reaches 6.5 with ultrapure water, product is dried at 90 DEG C, obtains support type Manganese Ferrite Adsorbent.
Embodiment 3
(1) 8.7g vinasse are weighed to mix with 100mL ultrapure water, 30min is stirred under the conditions of 25 DEG C, makes vinasse substantially uniformity Be dispersed in water, then by 4.46gMnCl2With 9.67g Fe (NO3)3It is added in spent wash, uses after the solid is completely dissolved The NaOH solution of 5mol/L adjusts the pH value of mixed liquor to 11, and mixed liquor is put into 70 DEG C of drying boxes and reacts 3h;
(2) it by the sediment generated in mixed liquor (support type Manganese Ferrite adsorbent precursors) after being separated in mixed liquor, uses Ultrapure water is cleaned multiple times, is filtered, the dry 20h at 110 DEG C, in N2It under environment, puts the precipitate in quartz boat, is put into With 800 DEG C of calcining 0.5h in the tube furnace of 5 DEG C/min of heating rate, it is fully crystallized metal;
(3) in N2It after being cooled to room temperature step (2) products therefrom under environment, is ground using agate mortar, crosses 100 mesh Sieve is repeatedly washed until the pH of cleaning solution reaches 7.0 with ultrapure water, product is dried at 110 DEG C, obtains support type Manganese Ferrite Adsorbent.
Embodiment 4
(1) 10g vinasse are weighed to mix with 100mL ultrapure water, 30min is stirred under the conditions of 25 DEG C, makes vinasse substantially uniformity Be dispersed in water, then by 2.5g MnCl2、3.38gMnSO4·4H2O and 12.9g FeCl3It is added in spent wash, to solid Body is adjusted the pH value of mixed liquor to 10.5 with the NaOH solution of 5mol/L after all dissolving, and mixed liquor is put into 55 DEG C of drying boxes Middle reaction 4h;
(2) it by the sediment generated in mixed liquor (support type Manganese Ferrite adsorbent precursors) after being separated in mixed liquor, uses Ultrapure water is cleaned multiple times, is filtered, the dry 20h at 80 DEG C, in N2It under environment, puts the precipitate in quartz boat, is put into With 400 DEG C of calcining 2h in the tube furnace of 5 DEG C/min of heating rate, it is fully crystallized metal;
(3) in N2It after being cooled to room temperature step (2) products therefrom under environment, is ground using agate mortar, crosses 100 mesh Sieve is repeatedly washed until the pH of cleaning solution reaches 6.5 with ultrapure water, product is dried at 80 DEG C, obtains support type Manganese Ferrite Adsorbent.
Embodiment 5
(1) 10g vinasse are weighed to mix with 100mL ultrapure water, 30min is stirred under the conditions of 25 DEG C, makes vinasse substantially uniformity Be dispersed in water, then by 5g MnCl2With 8g Fe2(SO4)3、10.8g FeCl3·6H2O is added in spent wash, to solid Body is adjusted the pH value of mixed liquor to 9.5 with the NaOH solution of 5mol/L after all dissolving, and mixed liquor is put into 40 DEG C of drying boxes Middle reaction 3h;
(2) it by the sediment generated in mixed liquor (support type Manganese Ferrite adsorbent precursors) after being separated in mixed liquor, uses Ultrapure water is cleaned multiple times, is filtered, the dry 20h at 90 DEG C, in N2It under environment, puts the precipitate in quartz boat, is put into With 600 DEG C of calcining 2h in the tube furnace of 5 DEG C/min of heating rate, it is fully crystallized metal;
(3) in N2After being cooled to room temperature step (2) products therefrom under environment, repeatedly washed with ultrapure water until cleaning solution PH reach 5.5, product is dried at 90 DEG C, obtains support type Manganese Ferrite adsorbent.
Comparative example 1
The preparation of support type Manganese Ferrite adsorbent is carried out in the way of embodiment 1, unlike, it is replaced using ferrous chloride Change ferric trichloride.
Comparative example 2
The preparation of support type Manganese Ferrite adsorbent is carried out in the way of embodiment 1, unlike, it is substituted using active carbon Vinasse.
Test case 1-7
Atoxylic acid solution concentration of standard solution used in test is 1000ppm (1000mg/L), other concentration Thus titer dilutes to obtain atoxylic acid solution, and 4- (dimethylamino) benzaldehyde solution is prepared by 1:9 hydrochloric acid solution, Test carries out in the polyethylene bottle of 100mL.
Prepare the atoxylic acid solution that 7 groups of 50mL concentration are 20mg/L.50mg reality is separately added into above-mentioned solution The support type Manganese Ferrite adsorbent for applying example and comparative example preparation, is adsorbed under the conditions of temperature is 25 DEG C, pH=2, sufficiently anti- Should after sample, by sample solution by the filtering of 0.45 μm of water system miillpore filter after, it is molten that 1mL 4- (dimethylamino) benzaldehyde is added Liquid calculates adsorption capacity and absorption with the concentration of the atoxylic acid solution after ultraviolet-uisible spectrophotometer measurement absorption Rate, the results are shown in Table 1.
It can be seen that the support type Manganese Ferrite adsorbent compared to comparative example 1-2 preparation by the result of table 1, using this The support type Manganese Ferrite adsorbent of invention preparation method has an adsorption effect of better atoxylic acid, and adsorption capacity compared with Height can effectively remove atoxylic acid in a short time.
Table 1
Number Adsorption capacity (mg/g) Adsorption rate (%)
Embodiment 1 18.00 89.33
Embodiment 2 17.12 84.00
Embodiment 3 16.66 82.27
Embodiment 4 16.00 80.08
Embodiment 5 15.07 75.43
Comparative example 1 11.36 55.74
Comparative example 2 11.16 55.51
Test case 8
Be respectively adopted the solution of different pH value, different sorption reaction times, different initial concentrations atoxylic acid, Different quantity of sorbent and different temperatures, support type Manganese Ferrite adsorbent prepared by testing example 1 is in adsorption aqueous solution The ability of atoxylic acid.Atoxylic acid solution concentration of standard solution used in test is 1000ppm (i.e. 1000mg/ L), thus titer dilutes to obtain the atoxylic acid solution of other concentration, and 4- (dimethylamino) benzaldehyde solution is by 1:9 Hydrochloric acid solution is prepared, and test carries out in the polyethylene bottle of 100mL.
1, influence of the pH value to support type Manganese Ferrite adsorbent adsorption capacity
Prepare the atoxylic acid solution that 10 groups of 50mL concentration are 20mg/L, uses 0.1mol/L HCl and 0.1mol/L The initial pH that NaOH adjusts solution is respectively 2.0,3.0,4.0,5.0,6.0,7.0,8.0,9.0,10.0,11.0, to above-mentioned molten The support type Manganese Ferrite adsorbent of the preparation of 50mg embodiment 1 is separately added into liquid, after sufficiently reaction is carried out under the conditions of 25 DEG C or so By sample solution by 0.45 μm of water system miillpore filter filtering 1mL 4- (dimethylamino) benzaldehyde solution is added, with purple in sampling Atoxylic acid solution concentration after outer visible spectrophotometer measurement absorption.Experimental result as shown in figure 3, when pH=2.0, The absorption of atoxylic acid is the most significant, and the support type Manganese Ferrite adsorbent that the raising of pH inhibits embodiment 1 to prepare is to right The absorption of atoxylate, at pH=2.0, adsorbent is 18mg/g, pH value to the maximum adsorption capacity of atoxylic acid When being increased to 3.0, adsorption capacity drops sharply to 6.67mg/g, and pH value range than more gentle between 5.0-11.0, hold by absorption Amount variation is little.
2, influence of the temperature to support type Manganese Ferrite adsorbent adsorption capacity
Prepare the atoxylic acid solution that 3 groups of 50mL concentration are 20mg/L.50mg reality is separately added into above-mentioned solution The support type Manganese Ferrite adsorbent for applying the preparation of example 1 is respectively placed under the conditions of 25 DEG C, 35 DEG C, 45 DEG C and pH=2.0 and is adsorbed, It is sufficiently sampled after reaction, after sample solution is filtered by 0.45 μm of water system miillpore filter, 1mL 4- (dimethylamino) benzene is added Formalin, with the concentration of the atoxylic acid solution after ultraviolet-uisible spectrophotometer measurement absorption.Experimental result such as Fig. 4 Shown, between 25 DEG C -35 DEG C, which has very big promotion to the adsorption rate of atoxylic acid, but at 35 DEG C -45 DEG C When, as the temperature rises, adsorption effect reduces instead, it will thus be seen that high temperature is not suitable for adsorption reaction.Test measures most Good laboratory scale adsorption reaction temperature is 35 DEG C, for the considerations of increasing difficulty to temperature in practical removal process, be may be selected 25 DEG C or adsorption test or adsorption applications are carried out under room temperature.
3, influence of the adsorption time to support type Manganese Ferrite adsorbent adsorption capacity
Prepare the atoxylic acid solution that 1 part of 50mL concentration is 20mg/L, 50mg embodiment 1 is added in Xiang Shangshu solution The support type Manganese Ferrite adsorbent of preparation is adsorbed under the conditions of temperature is 25 DEG C, pH=2, primary every 40min sampling, After sample solution is filtered by 0.45 μm of water system miillpore filter, 1mL 4- (dimethylamino) benzaldehyde solution is added, use is ultraviolet Atoxylic acid solution concentration after visible spectrophotometer measurement absorption.Experimental result as shown in figure 5, in preceding 360min, The removal rate of atoxylic acid is very fast, and support type Manganese Ferrite adsorbent is completely dissolved in atoxylic acid foul solution at this time In, be conducive to quick adsorption, with the growth of time, the removal rate of atoxylic acid is gradually gentle, reaches suction in 1440min Attached balance, removal rate have reached 86.43%.
4, influence of the initial concentration of atoxylic acid to support type Manganese Ferrite adsorbent adsorption capacity
Prepare the atoxylic acid solution of 9 groups of 50mL, initial concentration be respectively 5mg/L, 10mg/L, 25mg/L, 30mg/L, 50mg/L, 75mg/L, 100mg/L, 200mg/L, 300mg/L are separately added into 50mg embodiment 1 in Xiang Shangshu solution The support type Manganese Ferrite adsorbent of preparation is adsorbed under the conditions of temperature is 25 DEG C, pH=2, is sufficiently sampled after reaction, by sample After product solution is by 0.45 μm of water system miillpore filter filtering, 1mL 4- (dimethylamino) benzaldehyde solution is added, uses UV, visible light The concentration of atoxylic acid solution after spectrophotometric determination absorption.Experimental result is as shown in fig. 6, with initial concentration It increases, removal rate has substantial degradation, and the initial concentration of atoxylic acid has the suction-operated of the adsorbent larger Influence.
5, influence of the adsorbent amount to support type Manganese Ferrite adsorbent adsorption capacity
Prepare the atoxylic acid solution that 6 groups of 50mL concentration are 20mg/L, is separately added into the support type of the preparation of embodiment 1 Manganese Ferrite adsorbent 10mg, 20mg, 30mg, 50mg, 70mg, 90mg are adsorbed under the conditions of temperature is 25 DEG C, pH=2, are filled It is sampled after dividing reaction, after sample solution is filtered by 0.45 μm of water system miillpore filter, 1mL 4- (dimethylamino) benzene first is added Aldehyde solution, with the concentration of the atoxylic acid solution after ultraviolet-uisible spectrophotometer measurement absorption.Experimental result such as Fig. 7 institute Show, with increasing for support type Manganese Ferrite adsorbent dosage, the removal rate of atoxylic acid is gradually increased, and residue is to amino Phenylarsine acid concentration gradually decreases, and when adsorbent dosage is 50mg, the removal rate of atoxylic acid reaches 84%, later with Dosage increases, and the ascensional range of removal rate tends towards stability.
The preferred embodiment of the present invention has been described above in detail, and still, the present invention is not limited thereto.In skill of the invention In art conception range, can with various simple variants of the technical solution of the present invention are made, including each technical characteristic with it is any its Its suitable method is combined, and it should also be regarded as the disclosure of the present invention for these simple variants and combination, is belonged to Protection scope of the present invention.

Claims (10)

1. a kind of preparation method of support type Manganese Ferrite adsorbent, which is characterized in that this method comprises:
(1) vinasse are mixed with containing manganous salt and trivalent iron salt mixed liquor, mixed condition make manganous salt and Trivalent iron salt forms Manganese Ferrite, and is carried on the vinasse, obtains support type Manganese Ferrite adsorbent precursors;
(2) after the support type Manganese Ferrite adsorbent precursors drying and roasting, support type Manganese Ferrite adsorbent is obtained.
2. the method according to claim 1, wherein it is 9- that the condition of mixing described in step (1), which includes: pH, 11, temperature be 50-70 DEG C, time 3-5h.
3. the method according to claim 1, wherein the trivalent iron salt based on 100 parts by weight in step (1), institute The dosage for stating vinasse is 30-90 parts by weight, and the dosage of the manganous salt is 15-70 parts by weight.
4. the method according to claim 1, wherein manganous salt described in step (1) be selected from manganese sulfate and/or Manganese chloride, the trivalent iron salt are selected from least one of iron chloride, ferric sulfate and ferric nitrate.
5. the method according to claim 1, wherein further including before the drying in step (2) to described negative Load type Manganese Ferrite adsorbent precursors are washed.
6. the method according to claim 1, wherein temperature dry described in step (2) be 90-110 DEG C, when Between be 20-30h, the condition of the roasting include: in an inert atmosphere, temperature be 600-800 DEG C, time 0.5-2h.
7. method as claimed in any of claims 1 to 6, which is characterized in that this method further includes to the load Type Manganese Ferrite adsorbent is ground, is washed, is dried, and final products are obtained.
8. the method according to the description of claim 7 is characterized in that the grinding includes by the support type Manganese Ferrite adsorbent Being ground to granularity is 100 mesh or more, and the condition of the washing includes using milli-Q water to the pH of cleaning solution for 6.5-7.0, The temperature of the drying is 90-110 DEG C.
9. the support type Manganese Ferrite adsorbent of the preparation of method described in any one of claim 1-8.
10. application of the support type Manganese Ferrite adsorbent as claimed in claim 9 in removing atoxylic acid.
CN201910218395.5A 2019-03-21 2019-03-21 The preparation method and application of support type Manganese Ferrite adsorbent Pending CN109759018A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910218395.5A CN109759018A (en) 2019-03-21 2019-03-21 The preparation method and application of support type Manganese Ferrite adsorbent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910218395.5A CN109759018A (en) 2019-03-21 2019-03-21 The preparation method and application of support type Manganese Ferrite adsorbent

Publications (1)

Publication Number Publication Date
CN109759018A true CN109759018A (en) 2019-05-17

Family

ID=66459669

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910218395.5A Pending CN109759018A (en) 2019-03-21 2019-03-21 The preparation method and application of support type Manganese Ferrite adsorbent

Country Status (1)

Country Link
CN (1) CN109759018A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114702961A (en) * 2022-03-17 2022-07-05 中南大学 Amorphous ferro-manganese colloidal material and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103482706A (en) * 2013-10-15 2014-01-01 大连交通大学 Hollow spherical nano manganese ferrite, and preparation method and application thereof
CN105771878A (en) * 2016-03-31 2016-07-20 辽宁大学 Ferro-manganese modified aluminum oxide adsorbent and application thereof in As (III) adsorption
CN106892515A (en) * 2017-01-23 2017-06-27 中国科学院生态环境研究中心 A kind of method that high concentration organo-arsenic wastewater treatment is reclaimed with arsenic resource
CN107384973A (en) * 2017-08-30 2017-11-24 青岛海澄知识产权事务有限公司 A kind of preparation method of support type biology ferro manganese composite oxides
CN109248655A (en) * 2018-10-17 2019-01-22 天津大学 A kind of method of preparation and use and application of magnetic carbon nano-tube

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103482706A (en) * 2013-10-15 2014-01-01 大连交通大学 Hollow spherical nano manganese ferrite, and preparation method and application thereof
CN105771878A (en) * 2016-03-31 2016-07-20 辽宁大学 Ferro-manganese modified aluminum oxide adsorbent and application thereof in As (III) adsorption
CN106892515A (en) * 2017-01-23 2017-06-27 中国科学院生态环境研究中心 A kind of method that high concentration organo-arsenic wastewater treatment is reclaimed with arsenic resource
CN107384973A (en) * 2017-08-30 2017-11-24 青岛海澄知识产权事务有限公司 A kind of preparation method of support type biology ferro manganese composite oxides
CN109248655A (en) * 2018-10-17 2019-01-22 天津大学 A kind of method of preparation and use and application of magnetic carbon nano-tube

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
SHUANGSHUANG LV ET AL.: "Rice hull/MnFe2O4 composite: Preparation, characterization and its rapid microwave-assisted COD removal for organic wastewater", 《JOURNAL OF HAZARDOUS MATERIALS》 *
彭云: "铁氧化物对有机胂类药物的吸附行为研究", 《中国优秀硕士学位论文全文数据库 工程科技I辑》 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114702961A (en) * 2022-03-17 2022-07-05 中南大学 Amorphous ferro-manganese colloidal material and preparation method and application thereof

Similar Documents

Publication Publication Date Title
Yin et al. Use of lanthanum/aluminum co-modified granulated attapulgite clay as a novel phosphorus (P) sorbent to immobilize P and stabilize surface sediment in shallow eutrophic lakes
CN109590022A (en) Stratiform UiO-66/g-C3N4The preparation method and application of/Ag composite material
CN108905976A (en) Manganese ion doping metal-organic framework materials and its preparation method and application
CN107081133B (en) Application of the porous organic matter as antibiotic adsorbent
CN111001390A (en) Composite metal organic adsorption material and preparation method thereof
Su et al. Significant enhancement of pesticide and organic dyes degradation by ion-exchange within a metal–organic framework
CN108671886A (en) A kind of magnetic active carbon adsorbent and the preparation method and application thereof based on abandoned biomass
CN104941594B (en) The preparation method of photocatalytic degradation sorbing material and application
CN109806844A (en) A kind of magnetic metal organic framework materials of dephosphorization and preparation method thereof
CN102500167B (en) Core-shell structure composite filter material for water treatment and preparation method thereof
CN106994333B (en) The preparation method of the cystamine modification biological charcoal of adsorbing heavy metal cadmium ion
CN108499516A (en) Support type arsenic adsorbent and its preparation method and application and the method for arsenic removing
CN113731369B (en) Modified metal organic framework material and preparation method and application thereof
CN109759018A (en) The preparation method and application of support type Manganese Ferrite adsorbent
CN111957299B (en) Functionalized copper-based MOFs material and preparation method and application thereof
CN109692665A (en) A kind of preparation method of N doping porous charcoal removal antibiotic adsorbent
CN109650585A (en) A kind of control method of pre- chlorine dioxide byproduct chlorite leaves
CN107398257A (en) A kind of preparation method and application of modified zeolite molecular sieve adsorption particle
CN107159094A (en) The method that magnetic magnesium hydroxide adsorbent removes tetracycline in waste water
CN106582500B (en) Adsorbable degradation Cr (VI) diatomite composite material of one kind and preparation method thereof
WO2016197397A1 (en) Preparation method and use of photocatalytic degradation-adsorption material
CN109701490A (en) Magnetic cobalt carbon attapulgite composite material and preparation method and application
CN109647336B (en) Composite adsorbent for efficiently removing heavy metal ions in wastewater and preparation method thereof
CN108975504B (en) Method for simultaneously removing nitrite and ammonia nitrogen by copper bismuthate-fullerene photocatalyst
CN108745415B (en) Poly-o-phenylenediamine modified AgCl/g-C3N4Composite photocatalyst and preparation and application thereof

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20190517