CN110038519A - A kind of processing method of acid waste water containing heavy metal - Google Patents

A kind of processing method of acid waste water containing heavy metal Download PDF

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CN110038519A
CN110038519A CN201910358637.0A CN201910358637A CN110038519A CN 110038519 A CN110038519 A CN 110038519A CN 201910358637 A CN201910358637 A CN 201910358637A CN 110038519 A CN110038519 A CN 110038519A
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waste water
heavy metal
acid waste
acid
containing heavy
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刘琼
王璐
何玉远
刘睿
李娟�
王小庆
黄向东
刘彩霞
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Luoyang Institute of Science and Technology
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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
    • 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
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or 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
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The present invention relates to a kind of processing methods of acid waste water containing heavy metal, the pH value of acid waste water is 1.0-3.5, the modified tree peony shell adsorbent material of iminodiacetic acid is added in acid waste water containing heavy metal, it is stirred under room temperature, carry out standing filtering after stir process, after separation of solid and liquid, supernatant reaches discharge standard, solid content nitric acid solution is eluted and is washed with deionized to neutrality, is reused after dry.Processing method of the invention has many advantages, such as at low cost, high-efficient, simple process, possesses preferable industrial applications prospect.

Description

A kind of processing method of acid waste water containing heavy metal
Technical field
The present invention relates to technical field of waste water processing, and in particular to a kind of processing method of acid waste water containing heavy metal.
Background technique
Non-ferrous metal industry exploits in metal mine, it is lower that a large amount of pH can be generated during ore dressing and smelting etc. and containing weight The acid waste water of metal.If not appropriately processed direct emission, it can not only corrode the bases such as sewer pipe, water conservancy project structure and set Apply, heavy metal ion therein also can serious polluted surface water, underground water or soil, influence growth, the breeding of animals and plants, thus Huge harm is caused to environmental quality and human health.Currently, processing acid waste water containing heavy metal method mainly has chemistry heavy Shallow lake method, ion-exchange, membrane separation process, absorption method and artificial swamp method etc..Wherein, absorption method is because having wide adaptation range, behaviour Make the features such as easy, processing capacity is big, gets more and more people's extensive concerning.One of an important factor for pH value is influence absorption property, At the low ph, H3O+Adsorption site is fought for heavy metal ion, while hindering the dissociation of active group, causes adsorbance It reduces.Therefore, absorption method is usually combined with neutralization precipitation method, to realize the row up to standard of acid waste water containing heavy metal processing It puts.But this undoubtedly will increase processing cost, while a large amount of waste residues generated are also easy to cause secondary pollution to environment.
Summary of the invention
The purpose of the present invention is deficiencies to solve above-mentioned technical problem, provide a kind of processing of acid waste water containing heavy metal Method.This method has many advantages, such as at low cost, high-efficient, simple process, possesses preferable industrial applications prospect.
The deficiency of the present invention to solve above-mentioned technical problem, used technical solution is: a kind of spent acidic containing heavy metal The processing method of water, the pH value of acid waste water are 1.0-3.5, and the modified tree peony shell adsorbent material of iminodiacetic acid is added to containing weight It in metal acid waste water, is stirred under room temperature, carries out standing filtering after stir process, after separation of solid and liquid, supernatant Reach discharge standard, solid content nitric acid solution is eluted and is washed with deionized to neutrality, reuses after dry.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: the adsorbent material adds Entering amount is 0.2-2g/L.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: when the stir process Mixing speed is 100-160rpm, mixing time 1-3h.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: the nitric acid solution it is dense Degree is 0.1-1.0mol/L.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: iminodiacetic acid is modified Tree peony shell adsorbent material the preparation method is as follows: by tree peony shell crush after with sodium hydroxide, epoxychloropropane, ethyl alcohol and deionization Water mixing, heating stirring reaction, the solid reacted is washed, it is dry after, the mixed of iminodiacetic acid and sodium carbonate is added Heating stirring in solution is closed, after reaction, solid product is collected, obtains adsorbent material after washed, dry.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: iminodiacetic acid is modified The preparation method of tree peony shell adsorbent material is specific as follows:
A, after taking tree peony shell deionized water to impregnate, wash, being dry, with crusher machine sieving is crushed, sieve takes the powder of 35-24 mesh;
B, it takes step a to sieve the tree peony shell powder taken, mixes, be heated to sodium hydroxide, epoxychloropropane, ethyl alcohol and deionized water 35 DEG C are stirred to react, the solid obtained after reaction is washed, it is dry after it is spare;
C, the solid after taking step b dry is added in the mixed solution of iminodiacetic acid and sodium carbonate, is heated to 65 DEG C of progress It is stirred to react, after reaction, collects solid product, the modified tree peony shell absorption of iminodiacetic acid is obtained after washed, dry Material.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: in the step b: every In 100-300mL deionized water be added 2-10g tree peony shell powder, 12-50g sodium hydroxide, 30-100mL epoxychloropropane and 20-80mL ethyl alcohol.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: the mixing of the step c The concentration of iminodiacetic acid is 20-80g/L in solution, and the concentration of sodium carbonate is 20-60g/L.
As a kind of advanced optimizing for processing method of acid waste water containing heavy metal of the invention: the tree peony shell is Feng Dan The seed shell of tree peony.
Beneficial effect
One, the present invention is using the modified tree peony shell adsorbent material of iminodiacetic acid to containing Cu2+、Pb2+And Cd2+The acid of heavy metal Property waste water is handled, and after treatment, pH value of waste water can rise to 6.0-7.0 from original 1.0-3.5, heavy metal Cu2+、 Pb2+And Cd2+Removal rate reach 90.0% or more;
Two, the modified tree peony shell adsorbent material of the iminodiacetic acid that the present invention uses utilizes surface using discarded tree peony shell as raw material Hydroxyl reactive group abundant passes sequentially through etherificate and amion acetic acidization reaction, is made a kind of and contains chelation group-N (CH2COO-)2, and the heavy-metal adsorption material that specific surface area is larger, pore structure is flourishing, the adsorbent material is to containing heavy metal acid Property waste water have good treatment effect;
Three, the present invention takes lower epoxidation reaction temperature (35 DEG C) in the preparation process of adsorbent material, preferable to protect Aromatic structure abundant in tree peony husk as raw material is stayed.Under strongly acidic conditions, the surface protonated delocalizedπelectron of adsorbent material with again Complex compound is formd between metal ion.Also, as pH value of waste water increases, the active group-N (CH on surface2COO-)2With again Chelate is further defined between metal ion.Therefore, adsorbent material prepared by the present invention under strongly acidic conditions, is still able to maintain Preferable adsorption effect;
Four, the adsorbent material that uses of the present invention is modified using tree peony shell as raw material, modified tree peony shell surface isoelectric point by 5.8 rise to 8.9, have stronger alkalinity, can neutralize the acid in effluent part.In addition, sodium ion existing for tree peony shell surface, with There is also ion exchanges between hydrogen ion in acid waste water, thus useless using the modified adsorbent material processing of the present invention After water, the pH value of waste water has raising by a relatively large margin, substantially close to neutrality.
Detailed description of the invention
Fig. 1 is the scanning electron microscope (SEM) photograph of tree peony husk as raw material in embodiment 1;
Fig. 2 is the scanning electron microscope (SEM) photograph that adsorbent material is made in embodiment 1;
Fig. 3 is the infrared spectrogram of tree peony husk as raw material and obtained adsorbent material in embodiment 1.
Specific embodiment
Further technical solution of the present invention is illustrated below in conjunction with specific embodiment.
Embodiment 1
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 20g/L, 15g/L and 10g/L, acid waste water pH value be 2.0, the amount of acid waste water is 50L, when processing, is added into waste water 10g adsorbent material stirs 1h, speed of agitator 100rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 0.1mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 97.3%, 95.8% and 93.9%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: by the 50g tree peony shell (seed of phoenix pellet tree peony Shell) it is added in three-necked bottle, 300g sodium hydroxide is added, 750mL epoxychloropropane, 500mL dehydrated alcohol and 2500mL are gone Ionized water, after being heated to 35 DEG C, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added Enter into the mixed solution of 20.0g/L iminodiacetic acid and 20.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 8h.It is cold But solid product is collected afterwards, and is washed with deionized to neutrality, obtains adsorbent material after 60 DEG C of vacuum drying 12h.
Electronic Speculum processing is scanned to tree peony husk as raw material and adsorbent material obtained, from figure 1 it appears that tree peony shell (PSC) the fine and close layer structure stacked, only a small amount of hole is presented in surface.It compares, adsorbent material (IDA- in Fig. 2 PSC) then there are a large amount of deeper ducts in surface, and the fold of inner wall protrusion is high-visible, provides advantageous item for absorption Part.
Infrared spectrum analysis is carried out to tree peony husk as raw material and adsorbent material obtained, from figure 3, it can be seen that tree peony shell (PSC) 1619cm in-1Place is-COO-Middle C=O asymmetric stretching vibration peak, modified blue shift 16cm-1And the intensity of absorption peak It significantly increases and 1412cm-1The appearance for locating C=O symmetrical stretching vibration peak in carboxyl, illustrates the surface adsorbent material (IDA-PSC) On have the formation of carboxylate.1117cm-1Place is the stretching vibration peak of C-O-C in aromatic ester, and modified vibration is reinforced, with tertiary amine groups Introduce related, these sufficiently show that iminodiacetic acid is successfully connected to tree peony shell surface.
Embodiment 2
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 50g/L, 40g/L and 30g/L, acid waste water pH value be 2.5, the amount of acid waste water is 20L, when processing, is added into waste water 20g adsorbent material stirs 1.5h, speed of agitator 120rpm under room temperature.After standing filtering, solid content and filter are obtained respectively Liquid.Solid content is eluted with 0.5mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 95.3%, 93.8% and 92.9%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: by the 50g tree peony shell (seed of phoenix pellet tree peony Shell) it is added in three-necked bottle, 400g sodium hydroxide is added, 800mL epoxychloropropane, 600mL dehydrated alcohol and 2000mL are gone Ionized water, after being heated to 35 DEG C, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added Enter into the mixed solution of 40.0g/L iminodiacetic acid and 30.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 16h. Solid product is collected after cooling, and is washed with deionized to neutrality, obtains adsorbent material after 60 DEG C of vacuum drying 12h.
Embodiment 3:
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 100g/L, 80g/L and 60g/L, acid waste water pH value be 3.5, the amount of acid waste water is 10L, when processing, is added into waste water 20g adsorbent material stirs 3h, speed of agitator 160rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 1.0mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 91.3%, 90.8% and 90.1%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: by the 100g tree peony shell (seed of phoenix pellet tree peony Shell) it is added in three-necked bottle, 500g sodium hydroxide is added, 1000mL epoxychloropropane, 800mL dehydrated alcohol and 3000mL are gone Ionized water, after being heated to 35 DEG C, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added Enter into the mixed solution of 80.0g/L iminodiacetic acid and 60.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react for 24 hours. Solid product is collected after cooling, and is washed with deionized to neutrality, obtains adsorbent material after 60 DEG C of vacuum drying 12h.
Embodiment 4:
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 100g/L, 80g/L and 60g/L, acid waste water pH value be 1.0, the amount of acid waste water is 10L, when processing, is added into waste water 20g adsorbent material (adsorbent material is the adsorbent material being prepared in embodiment 1), stirs 3h, speed of agitator under room temperature For 160rpm.After standing filtering, solid content and filtrate are obtained respectively.Solid content eluted with 1.0mol/L nitric acid solution and spend from Sub- water washing is reusable after dry to neutrality.Filtrate measures concentration of heavy metal ion with ICP-MS, calculates and knows Cu2+、 Pb2+And Cd2+Removal rate be respectively 90.9%, 90.3% and 90.0%.
Embodiment 5:
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 20g/L, 15g/L and 10g/L, acid waste water pH value be 2.0, the amount of acid waste water is 50L, when processing, is added into waste water 10g adsorbent material stirs 1h, speed of agitator 100rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 0.1mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 76.3%, 70.8% and 66.9%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: 50g tree peony shell is added in three-necked bottle, 300g sodium hydroxide is added, 750mL epoxychloropropane, 500mL dehydrated alcohol and 2500mL deionized water are heated to 75 DEG C Afterwards, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added to 20.0g/L imino group In the mixed solution of oxalic acid and 20.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 8h.Solid product is collected after cooling, And be washed with deionized to neutrality, adsorbent material is obtained after 60 DEG C of vacuum drying 12h.
Embodiment 6:
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 20g/L, 15g/L and 10g/L, acid waste water pH value be 2.0, the amount of acid waste water is 50L, when processing, is added into waste water 10g adsorbent material stirs 1h, speed of agitator 100rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 0.1mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 58.2%, 40.1% and 39.6%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: 50g tree peony shell is added in three-necked bottle, 300g sodium hydroxide is added, 750mL epoxychloropropane, 500mL dehydrated alcohol and 2500mL deionized water are heated to 100 DEG C Afterwards, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added to 20.0g/L imino group In the mixed solution of oxalic acid and 20.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 8h.Solid product is collected after cooling, And be washed with deionized to neutrality, adsorbent material is obtained after 60 DEG C of vacuum drying 12h.
Embodiment 7
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 20g/L, 15g/L and 10g/L, acid waste water pH value be 2.0, the amount of acid waste water is 50L, when processing, is added into waste water 10g adsorbent material stirs 1h, speed of agitator 100rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 0.1mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 94.5%, 92.9% and 91.8%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: by the 50g tree peony shell (seed of Shandong pink peony Shell) it is added in three-necked bottle, 300g sodium hydroxide is added, 750mL epoxychloropropane, 500mL dehydrated alcohol and 2500mL are gone Ionized water, after being heated to 35 DEG C, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added Enter into the mixed solution of 20.0g/L iminodiacetic acid and 20.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 8h.It is cold But solid product is collected afterwards, and is washed with deionized to neutrality, obtains adsorbent material after 60 DEG C of vacuum drying 12h.
Embodiment 8
A kind of processing method of acid waste water containing heavy metal, Cu in the acid waste water of processing2+、Pb2+And Cd2+Concentration is respectively 20g/L, 15g/L and 10g/L, acid waste water pH value be 2.0, the amount of acid waste water is 50L, when processing, is added into waste water 10g adsorbent material stirs 1h, speed of agitator 100rpm under room temperature.After standing filtering, solid content and filtrate are obtained respectively. Solid content is eluted with 0.1mol/L nitric acid solution and is washed with deionized to neutrality, reusable after dry.Filtrate is used ICP-MS measures concentration of heavy metal ion, calculates and knows Cu2+、Pb2+And Cd2+Removal rate be respectively 94.2%, 92.1% and 91.3%。
The modified tree peony shell adsorbent material of iminodiacetic acid the preparation method comprises the following steps: by the 50g tree peony shell (seed of chrysanthemum certain herbaceous plants with big flowers tree peony Shell) it is added in three-necked bottle, 300g sodium hydroxide is added, 750mL epoxychloropropane, 500mL dehydrated alcohol and 2500mL are gone Ionized water, after being heated to 35 DEG C, mechanical stirring 6h.Product is washed through deionized water to neutrality, after 60 DEG C of vacuum drying 12h, is added Enter into the mixed solution of 20.0g/L iminodiacetic acid and 20.0g/L sodium carbonate.After being heated to 65 DEG C, it is stirred to react 8h.It is cold But solid product is collected afterwards, and is washed with deionized to neutrality, obtains adsorbent material after 60 DEG C of vacuum drying 12h.
The above described is only a preferred embodiment of the present invention, be not intended to limit the present invention in any form, though So the present invention has been disclosed as a preferred embodiment, and however, it is not intended to limit the invention, any technology people for being familiar with this profession Member, without departing from the scope of the present invention, when the technology contents using the disclosure above make out a little change or repair Decorations are the equivalent embodiment of equivalent variations, but without departing from the technical solutions of the present invention, according to the technical essence of the invention Any simple modification, equivalent change and modification to the above embodiments, all of which are still within the scope of the technical scheme of the invention.

Claims (9)

1. a kind of processing method of acid waste water containing heavy metal, the pH value of acid waste water is 1.0-3.5, it is characterised in that: will be sub- The modified tree peony shell adsorbent material of aminodiacetic acid adds in acid waste water containing heavy metal, is stirred, stirs under room temperature Carry out standing filtering after processing, after separation of solid and liquid, supernatant reaches discharge standard, solid content nitric acid solution elute and spend from Sub- water washing is reused after dry to neutrality.
2. a kind of processing method of acid waste water containing heavy metal as described in claim 1, it is characterised in that: the adsorbent material Additional amount is 0.2-2g/L.
3. a kind of processing method of acid waste water containing heavy metal as described in claim 1, it is characterised in that: when the stir process Mixing speed be 100-160rpm, mixing time 1-3h.
4. a kind of processing method of acid waste water containing heavy metal as described in claim 1, it is characterised in that: the nitric acid solution Concentration is 0.1-1.0 mol/L.
5. a kind of processing method of acid waste water containing heavy metal as described in claim 1, it is characterised in that: iminodiacetic acid changes Property tree peony shell adsorbent material the preparation method is as follows: by tree peony shell crush after with sodium hydroxide, epoxychloropropane, ethyl alcohol and go from The mixing of sub- water, heating stirring reaction, the solid reacted is washed, it is dry after, iminodiacetic acid and sodium carbonate is added Heating stirring in mixed solution collects solid product, obtains adsorbent material after washed, dry after reaction.
6. a kind of processing method of acid waste water containing heavy metal as claimed in claim 5, it is characterised in that: preparation method is specifically such as Under:
A, after taking tree peony shell deionized water to impregnate, wash, being dry, with crusher machine sieving is crushed, sieve takes the powder of 35-24 mesh;
B, it takes step a to sieve the tree peony shell powder taken, mixes, be heated to sodium hydroxide, epoxychloropropane, ethyl alcohol and deionized water 35 DEG C are stirred to react, the solid obtained after reaction is washed, it is dry after it is spare;
C, the solid after taking step b dry is added in the mixed solution of iminodiacetic acid and sodium carbonate, is heated to 65 DEG C of progress It is stirred to react, after reaction, collects solid product, the modified tree peony shell absorption of iminodiacetic acid is obtained after washed, dry Material.
7. a kind of processing method of acid waste water containing heavy metal as claimed in claim 6, it is characterised in that: in the step b: every In 100-300mL deionized water be added 2-10g tree peony shell powder, 12-50g sodium hydroxide, 30-100mL epoxychloropropane and 20-80mL ethyl alcohol.
8. a kind of processing method of acid waste water containing heavy metal as claimed in claim 6, it is characterised in that: the step c's is mixed The concentration for closing iminodiacetic acid in solution is 20-80g/L, and the concentration of sodium carbonate is 20-60g/L.
9. the processing method of acid waste water containing heavy metal as described in any claim in claim 5-8, it is characterised in that: institute State the seed shell that tree peony shell is phoenix pellet tree peony.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113117646A (en) * 2019-12-30 2021-07-16 Tcl集团股份有限公司 Composite material and preparation method thereof and purification method of quantum dots

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101077795A (en) * 2006-05-22 2007-11-28 北京化工大学 Composite biological adsorption and preparing method thereof
CN101249990A (en) * 2008-03-11 2008-08-27 东华大学 Method for rapidly removing metal copper ion from waste water
US20110003941A1 (en) * 2007-07-09 2011-01-06 Ge Healthcare Bio-Sciences Ab Method for preparation of a biomolecule adsorbent
CN103042023A (en) * 2012-12-20 2013-04-17 菏泽瑞璞牡丹产业科技发展有限公司 Comprehensive utilization method of peony shells

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101077795A (en) * 2006-05-22 2007-11-28 北京化工大学 Composite biological adsorption and preparing method thereof
US20110003941A1 (en) * 2007-07-09 2011-01-06 Ge Healthcare Bio-Sciences Ab Method for preparation of a biomolecule adsorbent
CN101249990A (en) * 2008-03-11 2008-08-27 东华大学 Method for rapidly removing metal copper ion from waste water
CN103042023A (en) * 2012-12-20 2013-04-17 菏泽瑞璞牡丹产业科技发展有限公司 Comprehensive utilization method of peony shells

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
QIONG LIU等: "Optimization and evaluation of alkali-pretreated Paeonia ostii seed coats as adsorbent for the removal of MB from aqueous solution", 《POLISH JOURNAL OF CHEMICAL TECHNOLOGY》 *
赵艳娇: "谷壳纤维素的改性及其对重金属离子吸附性能的研究", 《中国优秀博硕士学位论文全文数据库(硕士)工程科技Ⅰ辑》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113117646A (en) * 2019-12-30 2021-07-16 Tcl集团股份有限公司 Composite material and preparation method thereof and purification method of quantum dots
CN113117646B (en) * 2019-12-30 2022-08-09 Tcl科技集团股份有限公司 Composite material and preparation method thereof and purification method of quantum dots

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Application publication date: 20190723