CN110975836A - Shaddock peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof - Google Patents

Shaddock peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof Download PDF

Info

Publication number
CN110975836A
CN110975836A CN201911332979.1A CN201911332979A CN110975836A CN 110975836 A CN110975836 A CN 110975836A CN 201911332979 A CN201911332979 A CN 201911332979A CN 110975836 A CN110975836 A CN 110975836A
Authority
CN
China
Prior art keywords
amino
mercapto
shaddock peel
adsorbent
triazole
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.)
Granted
Application number
CN201911332979.1A
Other languages
Chinese (zh)
Other versions
CN110975836B (en
Inventor
纪红兵
熊超
薛灿
周贤太
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.)
National Sun Yat Sen University
Original Assignee
National Sun Yat Sen 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 National Sun Yat Sen University filed Critical National Sun Yat Sen University
Priority to CN201911332979.1A priority Critical patent/CN110975836B/en
Publication of CN110975836A publication Critical patent/CN110975836A/en
Application granted granted Critical
Publication of CN110975836B publication Critical patent/CN110975836B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • 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
    • B01J20/22Solid 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The invention discloses a 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent and a preparation method and application thereof, and belongs to the field of adsorbent preparation. Firstly, drying shaddock peel, performing ball milling to obtain powder, and activating by concentrated sulfuric acid to obtain PP-SC. Then reacting with chloroacetyl chloride under anhydrous condition to obtain PP-CC. And finally, carrying out reflux reaction on PP-CC and 3-amino-5-mercapto-1, 2, 4-triazole to obtain the PP-ATT adsorbent. The preparation method of the adsorbent is simple and feasible, the operation is simple and convenient, and the raw materials are cheap and easy to obtain. The obtained novel shaddock peel modified material has high-efficiency and high-selectivity effects on removal of lead ions in an aqueous solution, and can be recycled. The invention provides a green and efficient adsorbent for treating the lead-containing wastewater, provides a method for recycling agricultural wastes, and brings a new idea for designing and synthesizing a novel adsorbent.

Description

Shaddock peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof
Technical Field
The invention relates to a 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent, and a preparation method and application thereof, and belongs to the technical field of adsorbent preparation.
Background
Lead (Pb) has long been listed as one of the most harmful pollutants by the world health organization due to its high toxicity, carcinogenicity, bioaccumulation, and non-degradability. With the development of industries such as battery manufacturing, petroleum refining, mineral deposit smelting, coating production and the like, a large amount of lead ions enter a water circulation system, and great threat is caused to organisms. After entering the human body by sucking, lead can cause irreversible damage to nerves, reproduction, brain, kidney, liver and blood systems; even at lower levels, the effect is more severe. Therefore, effective measures are necessary to control lead contamination. Meanwhile, lead is widely used in industry due to its low melting point, corrosion resistance, and heavy plasticity. Therefore, the recovery of lead is also an important issue in the field of engineering for environmental and materials. At present, the main lead removal methods include precipitation, biological, electrochemical, ion exchange and adsorption. The chemical precipitation method can generate secondary pollution and has poor selectivity; biological methods are limited by the fact that specialized microorganisms are few in species and short in life; ion exchange methods and electrochemical methods are relatively costly and have poor reproducibility. The adsorption method is considered to be one of the most effective methods due to the advantages of simple operation, repeatability, selectivity, no secondary pollution and the like. The common adsorbents include activated carbon, resin, natural minerals, agricultural and sideline products, silicon dioxide and the like. The shaddock peel is agricultural waste, and is usually treated by landfill and incineration, so that resource waste and environmental pollution are caused. However, the shaddock peel is rich in amino and hydroxyl and is a post-modified high-quality low-cost material.
Disclosure of Invention
Aiming at the problems and the defects in the prior art, the invention aims to provide a preparation method and application of a 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent. The modified shaddock peel adsorbent can be used for selectively removing lead ions in an acidic aqueous solution, is low in material cost, simple in synthesis process, easy to separate from the aqueous solution, high in adsorption capacity and reusable.
The invention is realized by the following technical scheme:
a3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent has a structural formula shown in formula (I):
Figure BDA0002330174130000021
wherein
Figure BDA0002330174130000022
Is a shaddock peel schematic structure with exposed hydroxyl/amino after being activated by concentrated sulfuric acid;
r is:
Figure BDA0002330174130000023
the invention also aims to provide a preparation method of the shaddock peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole, which comprises the following steps:
(1) cutting the pomelo peel into small pieces, drying, and grinding into powder by using a small ball mill; the preparation method comprises the steps of putting shaddock peel powder into a beaker, adding 98 wt% concentrated sulfuric acid for pretreatment, transferring the shaddock peel powder into a round-bottom three-neck flask, performing reflux stirring and activation treatment at 100 ℃ to expose surface functional groups, performing liquid-solid separation after reflux, washing the obtained solid to be neutral by deionized water, and drying to obtain a product PP-SC, wherein the reaction flow is shown in figure 1.
(2) In an anhydrous environment, sequentially adding the PP-SC product obtained in the step (1) and chloroacetyl chloride into an N, N-dimethylformamide solution for reflux reaction, performing liquid-solid separation, washing the obtained solid with the N, N-dimethylformamide solution, centrifuging, and performing vacuum drying to obtain a product PP-CC; the reaction route is as follows:
Figure BDA0002330174130000024
(3) under the protection of nitrogen, sequentially adding the PP-CC product obtained in the step (2) and 3-amino-5-mercapto-1, 2, 4-triazole into N, N-dimethylformamide for reflux reaction, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, and carrying out vacuum drying to obtain a PP-ATT product; the synthesis route is as follows:
Figure BDA0002330174130000031
preferably, in the above production method: in the step (1), the liquid-solid ratio of the concentrated sulfuric acid to the shaddock peel powder is 3: 1-7: 1 mL/g.
Preferably, in the above production method: in the step (2), the liquid-solid ratio of the N, N-dimethylformamide to the PP-SC is 30: 1-50: 1mL/g, and the liquid-solid ratio of the chloroacetyl chloride to the PP-SC is 5: 3-10: 3.
Preferably, in the above production method: in the step (3), the liquid-solid ratio of the N, N-dimethylformamide to the PP-CC is 40: 1-56: 1mL/g, and the mass ratio of the 3-amino-5-mercapto-124 triazole to the PP-CC is 2: 5-1: 1.
Preferably, in the above production method: in the step (1), the reflux is carried out for 5-15 h at 50-100 ℃; in the step (2), the reflux is carried out for 12-24 h at the temperature of 80-100 ℃; in the step (3), the reflux is carried out for 12-24 hours at the temperature of 45-85 ℃.
The 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent is applied to selective adsorption removal of lead ions in an acidic aqueous solution.
The organic and inorganic reagents were commercially available analytical grade.
Compared with the prior art, the invention has the following beneficial effects:
(1) the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent has good selectivity, high adsorption quantity and excellent removal rate on lead ion adsorption.
(2) The adsorbent of the invention has simple preparation process, easy synthesis and low cost of raw materials.
(3) The 3-amino-5-mercapto-1, 2,4 triazole modified shaddock peel adsorbent is non-toxic, stable in performance, easy to separate, reusable and free of secondary pollution to the environment.
(4) The modified shaddock peel adsorbent has good economic and practical values. Has great popularization potential in the aspects of selective removal and recovery of lead ions in aqueous solution.
Drawings
FIG. 1 is a schematic view of the reaction scheme of step (1).
Detailed Description
The present invention will be further described with reference to the following embodiments.
Example 1:
the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent has a structural formula as follows:
Figure BDA0002330174130000041
wherein
Figure BDA0002330174130000042
Is a shaddock peel schematic structure with exposed hydroxyl/amino after being activated by concentrated sulfuric acid;
r is:
Figure BDA0002330174130000043
the preparation method of the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent comprises the following specific steps:
(1) cutting pericarpium Citri Grandis into pieces of about 1cm, oven drying, and grinding into powder with small ball mill. Taking 10g of shaddock peel powder into a 1L beaker, adding 98 wt% concentrated sulfuric acid according to the liquid-solid ratio of 3:7 of concentrated sulfuric acid to the shaddock peel powder, pretreating for 3h, transferring the mixture into a round-bottom three-neck flask, refluxing for 5h at 50 ℃ to activate surface functional groups, carrying out liquid-solid separation after the reaction is finished, washing the obtained solid to be neutral by deionized water, and carrying out centrifugal drying to obtain a product PP-SC; the reaction scheme is shown in FIG. 1.
(2) Under an anhydrous environment, uniformly mixing an N, N-dimethylformamide solution and PP-SC according to a liquid-solid ratio of 30:1mL/g, adding chloroacetyl chloride according to a liquid-solid ratio of 5:3 of chloroacetyl chloride to PP-SC, carrying out reflux reaction for 12h at the temperature of 80 ℃, carrying out liquid-solid separation, washing and centrifuging the obtained solid by using N, N-dimethylformamide, and carrying out vacuum drying to obtain a product PP-CC; the synthetic route is as follows:
Figure BDA0002330174130000044
(3) under the nitrogen protection environment, uniformly mixing PP-CC obtained in the step (2) with N, N-dimethylformamide according to the solid-to-liquid ratio of 1:40g/mL, adding 3-amino-5-mercapto-1, 2, 4-triazole according to the mass ratio of 3-amino-5-mercapto-1, 2, 4-triazole to PP-CC of 2:5, carrying out reflux reaction for 12 hours at 45 ℃, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, centrifuging and drying to obtain a product PP-ATT; the synthetic route is as follows:
Figure BDA0002330174130000051
and (3) measuring the lead ion adsorption performance:
10mg of PP-ATT in the example is put into a lead ion solution with the initial concentration of 200mg/L for oscillation adsorption for 2h, centrifugal separation is carried out, the concentration of the residual lead ions in the supernatant is measured by ICP-OES to be 19.7mg/L, and the adsorption rate is 90.15%. Desorbing the bottom layer solid with thiourea solution (10 wt%) for 12h, washing for 3 times, drying at 65 deg.C for 24h, adding into 200mg/L lead ion solution again, shaking for adsorption for 2h, centrifuging, and measuring the residual lead ion concentration in the supernatant to be 23.12mg/L and the adsorption rate to be 88.44%. The 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent PP-ATT can be repeatedly used for removing lead ions in an aqueous solution.
Example 2:
the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent has a structural formula as follows:
Figure BDA0002330174130000052
wherein
Figure BDA0002330174130000053
Is a shaddock peel schematic structure with exposed hydroxyl/amino after being activated by concentrated sulfuric acid;
r is:
Figure BDA0002330174130000054
The preparation method of the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent comprises the following specific steps:
(1) cutting pericarpium Citri Grandis into pieces of about 1cm, oven drying, and grinding into powder with small ball mill. Putting 10g of shaddock peel powder into a 1L beaker, adding 98 wt% concentrated sulfuric acid according to the liquid-solid ratio of 5:7 of concentrated sulfuric acid to the shaddock peel powder, pretreating for 3h, transferring the mixture into a round-bottom three-neck flask, refluxing for 10h at 75 ℃ to activate surface functional groups, carrying out liquid-solid separation after the reaction is finished, washing the obtained solid to be neutral by deionized water, and drying to obtain a product PP-SC; the reaction scheme is shown in figure 1
(2) Under an anhydrous environment, uniformly mixing an N, N-dimethylformamide solution and PP-SC according to a liquid-solid ratio of 40:1mL/g, adding chloroacetyl chloride according to a liquid-solid ratio of 5:2 of chloroacetyl chloride to PP-SC, carrying out reflux reaction for 18h at 90 ℃, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, centrifuging, and carrying out vacuum drying to obtain a product PP-CC; the synthetic route is as follows:
Figure BDA0002330174130000061
(3) under the nitrogen protection environment, uniformly mixing PP-CC obtained in the step (2) with N, N-dimethylformamide according to the solid-liquid ratio of 1:48g/mL, adding 3-amino-5-mercapto-1, 2, 4-triazole according to the mass ratio of 7:10 of 3-amino-5-mercapto-1, 2, 4-triazole to PP-CC, carrying out reflux reaction at 85 ℃ for 18h, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, centrifuging and drying to obtain a product PP-ATT; the synthetic route is as follows:
Figure BDA0002330174130000062
and (3) measuring the lead ion adsorption performance:
10mg of PP-ATT adsorbent in the example is put into a lead ion solution with the initial concentration of 200mg/L for oscillation adsorption for 2h, centrifugal separation is carried out, the concentration of the residual lead ions in the supernatant is measured by ICP-OES to be 13.34mg/L, and the adsorption rate is 93.33%. Desorbing the bottom layer solid with thiourea solution (10 wt%) for 12h, washing, drying at 65 deg.C for 24h, adding into 200mg/L lead ion solution again, shaking for 2h, centrifuging, and measuring the residual lead ion concentration in the supernatant as 16.38mg/L and the adsorption rate as 91.81%. The 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent PP-ATT can be repeatedly used for removing lead ions in an aqueous solution.
Example 3:
the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent has a structural formula as follows:
Figure BDA0002330174130000071
wherein
Figure BDA0002330174130000072
Is a shaddock peel schematic structure with exposed hydroxyl/amino after being activated by concentrated sulfuric acid;
r is:
Figure BDA0002330174130000073
the preparation method of the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent comprises the following specific steps:
(1) cutting pericarpium Citri Grandis into pieces of about 1cm, oven drying, and grinding into powder with small ball mill. 10g of shaddock peel powder is taken to be put into a 1L beaker, and 98 wt% concentrated sulfuric acid is added according to the liquid-solid ratio of concentrated sulfuric acid to shaddock peel powder of 7:1 for pretreatment for 3 hours. Transferring the mixture into a round bottom three-neck flask, refluxing for 15h at 100 ℃ to activate surface functional groups, carrying out liquid-solid separation after the reaction is finished, washing the obtained solid to be neutral by using deionized water, and drying to obtain a product PP-SC; the reaction scheme is shown in FIG. 1.
(2) Under an anhydrous environment, uniformly mixing an N, N-dimethylformamide solution and PP-SC according to a liquid-solid ratio of 50:1mL/g, adding chloroacetyl chloride according to a liquid-solid ratio of 10:3 of chloroacetyl chloride to PP-SC, carrying out reflux reaction for 24 hours at 100 ℃, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, centrifuging, and carrying out vacuum drying to obtain a product PP-CC; the specific synthetic route is as follows:
Figure BDA0002330174130000081
(3) under the nitrogen protection environment, uniformly mixing PP-CC obtained in the step (2) with N, N-dimethylformamide according to the solid-to-liquid ratio of 1:56g/mL, adding 3-amino-5-mercapto-1, 2, 4-triazole according to the mass ratio of 1:1 of 3-amino-5-mercapto-1, 2, 4-triazole to PP-CC, carrying out reflux reaction at 65 ℃ for 24 hours, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, centrifuging and drying to obtain a product PP-ATT; the specific synthetic route is as follows:
Figure BDA0002330174130000082
and (3) measuring the lead ion adsorption performance:
10mg of PP-ATT adsorbent in the embodiment is put into a lead ion solution with the initial concentration of 200mg/L for oscillation adsorption for 2h, centrifugal separation is carried out, the concentration of the residual lead ions in the supernatant is measured by ICP-OES to be 2.04mg/L, and the adsorption rate is 98.98%. Desorbing the bottom layer solid with thiourea solution (10 wt%) for 12h, centrifuging, washing, drying at 65 deg.C for 24h, adding into 200mg/L lead ion solution, shaking for 2h, centrifuging, and measuring the residual lead ion concentration in the supernatant to be 3.57mg/L and the adsorption rate to be 98.22%. The 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent PP-ATT can be repeatedly used for removing lead ions in an aqueous solution.
While the present invention has been described in detail with reference to the specific embodiments thereof, the present invention is not limited to the embodiments described above, and various changes can be made without departing from the spirit of the present invention within the knowledge of those skilled in the art.

Claims (7)

1. The 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent is characterized in that the structural formula is shown as the formula (I):
Figure FDA0002330174120000011
wherein
Figure FDA0002330174120000012
Is a shaddock peel schematic structure with exposed hydroxyl/amino after being activated by concentrated sulfuric acid;
r is:
Figure FDA0002330174120000013
2. the preparation method of the 3-amino-5-mercapto-1, 2, 4-triazole modified shaddock peel adsorbent as claimed in claim 1, is characterized by comprising the following steps:
(1) cutting the pomelo peel into small pieces, drying, and grinding into powder by using a small ball mill; putting the shaddock peel powder into a beaker, adding 98 wt% concentrated sulfuric acid for pretreatment, transferring the shaddock peel powder to a round-bottom three-neck flask, performing reflux stirring and activation treatment at 100 ℃ to expose surface functional groups, performing liquid-solid separation after reflux, washing the obtained solid to be neutral by using deionized water, and drying to obtain a product PP-SC;
(2) in an anhydrous environment, sequentially adding the PP-SC product obtained in the step (1) and chloroacetyl chloride into an N, N-dimethylformamide solution for reflux reaction, performing liquid-solid separation, washing the obtained solid with the N, N-dimethylformamide solution, centrifuging, and performing vacuum drying to obtain a product PP-CC;
(3) and (3) under the protection of nitrogen, sequentially adding the PP-CC product obtained in the step (2) and 3-amino-5-mercapto-1, 2, 4-triazole into N, N-dimethylformamide for reflux reaction, carrying out liquid-solid separation, washing the obtained solid with N, N-dimethylformamide, and carrying out vacuum drying to obtain the PP-ATT product.
3. The method of claim 2, wherein: in the step (1), the liquid-solid ratio of the concentrated sulfuric acid to the shaddock peel powder is 3: 1-7: 1 mL/g.
4. The method of claim 2, wherein: in the step (2), the liquid-solid ratio of the N, N-dimethylformamide to the PP-SC is 30: 1-50: 1mL/g, and the liquid-solid ratio of the chloroacetyl chloride to the PP-SC is 5: 3-10: 3.
5. The method of claim 2, wherein: in the step (3), the liquid-solid ratio of the N, N-dimethylformamide to the PP-CC is 40: 1-56: 1mL/g, and the mass ratio of the 3-amino-5-mercapto-1, 2, 4-triazole to the PP-CC is 2: 5-1: 1.
6. The method of claim 2, wherein: the reflux in the step (1) is carried out for 5-15 h at the temperature of 50-100 ℃; the reflux in the step (2) is carried out for 12-24 h at the temperature of 80-100 ℃; in the step (3), the reflux is carried out for 12-24 h at the temperature of 45-85 ℃.
7. The application of the 3-amino-5-mercapto-1, 2, 4-triazole modified pomelo peel adsorbent in claim 1 in selective adsorption and removal of lead ions in acidic aqueous solution.
CN201911332979.1A 2019-12-23 2019-12-23 Pomelo peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof Active CN110975836B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201911332979.1A CN110975836B (en) 2019-12-23 2019-12-23 Pomelo peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201911332979.1A CN110975836B (en) 2019-12-23 2019-12-23 Pomelo peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN110975836A true CN110975836A (en) 2020-04-10
CN110975836B CN110975836B (en) 2023-01-17

Family

ID=70074557

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201911332979.1A Active CN110975836B (en) 2019-12-23 2019-12-23 Pomelo peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN110975836B (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016187796A1 (en) * 2015-05-21 2016-12-01 江南大学 Preparation method and use of heavy metal ion adsorbent
CN106582535A (en) * 2016-11-30 2017-04-26 昆明理工大学 Modified silicon dioxide nanoparticle adsorbent and preparation method and application thereof
CN106824108A (en) * 2017-01-23 2017-06-13 四川大学 A kind of preparation method of the functionalization hydro-thermal carbon material for for uranium in solution separate
CN108160049A (en) * 2018-01-08 2018-06-15 昆明理工大学 It is a kind of to be used to adsorb modified corn shell adsorbent of gold ion and its preparation method and application

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016187796A1 (en) * 2015-05-21 2016-12-01 江南大学 Preparation method and use of heavy metal ion adsorbent
CN106582535A (en) * 2016-11-30 2017-04-26 昆明理工大学 Modified silicon dioxide nanoparticle adsorbent and preparation method and application thereof
CN106824108A (en) * 2017-01-23 2017-06-13 四川大学 A kind of preparation method of the functionalization hydro-thermal carbon material for for uranium in solution separate
CN108160049A (en) * 2018-01-08 2018-06-15 昆明理工大学 It is a kind of to be used to adsorb modified corn shell adsorbent of gold ion and its preparation method and application

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
SRINU NAGIREDDI,ET AL: "Role of EDTA on the Pd (II) adsorption characteristics of chitosan cross-linked 3-amino-1,2,4-triazole-5-thiol derivative from synthetic electroless plating solutions", 《INTERNATIONAL JOURNAL OF BIOLOGICAL MACROMOLECULES》 *
王琼等: "生物质废弃物柚子皮作为潜在吸附剂用于废水处理", 《湖南工业大学学报》 *

Also Published As

Publication number Publication date
CN110975836B (en) 2023-01-17

Similar Documents

Publication Publication Date Title
CN110813244B (en) Modified zirconium-based organic metal framework adsorbent for adsorbing lead ions and preparation method and application thereof
CN107188330B (en) Method for adsorbing and purifying acidic wastewater
Volesky Removal and recovery of heavy metals by biosorption
Hammaini et al. Biosorption of heavy metals by activated sludge and their desorption characteristics
Zamboulis et al. Metal ion separation and recovery from environmental sources using various flotation and sorption techniques
CN102151546B (en) Modified zeolite as well as preparation method and application thereof
CN100402141C (en) Preparation method of modified turf adsorbent
CN108929693A (en) A kind of soil heavy metal combined passivator and its application method
CN112569900A (en) Preparation method and application of novel municipal sludge biochar
Low et al. Effect of dye modification on the sorption of copper by coconut husk
CN113820187A (en) Passivation experiment method for applying attapulgite-rice straw composite material to heavy metal contaminated soil
CN110975836B (en) Pomelo peel adsorbent modified by 3-amino-5-mercapto-1, 2, 4-triazole and preparation method and application thereof
CN105174355B (en) A kind of method that utilization clay mineral removes metal ion in acid waste water
CN110436728B (en) Method for in-situ stabilization repair of lead-polluted bottom mud by iron-based material and microorganisms
CN111001392A (en) Preparation method and application of modified zirconium-based metal organic framework adsorbent for gold ion adsorption
CN108892342B (en) Preparation method of composite material for fixing heavy metals in water body sediment
CN110813248B (en) O-dihydroxybenzaldehyde modified shaddock peel adsorbent and preparation method and application thereof
CN113145075A (en) Preparation method and application of lanthanum-modified sludge biochar
Jin et al. Distribution of Pb and its chemical fractions in liquid and solid phases of digested pig and dairy slurries
CN111534507A (en) Immobilized microbial agent for raw ore of clay mineral, preparation method and application
Zouboulis et al. Biosorptive flotation for metal ions recovery
CN112774621B (en) Hollow microsphere and preparation method and application thereof
Pundir et al. Recovery of Cu and Ni ions from metals-loaded fungal biomass using acidic eluent
Cho et al. Biosorption of copper by immobilized biomass of Pseudomonas stutzeri
CN108993387A (en) A kind of method of contents of many kinds of heavy metal ion in the carbon-based magnetic material Adsorption waste water of fluorine doped

Legal Events

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