CN109985645A - A kind of hollow Porous HAP microballoon composite material of CdS/ and its preparation and application - Google Patents

A kind of hollow Porous HAP microballoon composite material of CdS/ and its preparation and application Download PDF

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Publication number
CN109985645A
CN109985645A CN201910308260.8A CN201910308260A CN109985645A CN 109985645 A CN109985645 A CN 109985645A CN 201910308260 A CN201910308260 A CN 201910308260A CN 109985645 A CN109985645 A CN 109985645A
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microballoon
cds
hollow porous
composite material
porous hap
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吴强
雷晓芳
徐天红
姚伟峰
齐雪梅
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Shanghai University of Electric Power
University of Shanghai for Science and Technology
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Shanghai University of Electric Power
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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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/024Compounds of Zn, Cd, Hg
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0285Sulfides of compounds other than those provided for in B01J20/045
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/048Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium containing phosphorus, e.g. phosphates, apatites, hydroxyapatites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/14Phosphorus; Compounds thereof
    • B01J27/16Phosphorus; Compounds thereof containing oxygen, i.e. acids, anhydrides and their derivates with N, S, B or halogens without carriers or on carriers based on C, Si, Al or Zr; also salts of Si, Al and Zr
    • B01J27/18Phosphorus; Compounds thereof containing oxygen, i.e. acids, anhydrides and their derivates with N, S, B or halogens without carriers or on carriers based on C, Si, Al or Zr; also salts of Si, Al and Zr with metals other than Al or Zr
    • B01J27/1802Salts or mixtures of anhydrides with compounds of other metals than V, Nb, Ta, Cr, Mo, W, Mn, Tc, Re, e.g. phosphates, thiophosphates
    • B01J27/1806Salts or mixtures of anhydrides with compounds of other metals than V, Nb, Ta, Cr, Mo, W, Mn, Tc, Re, e.g. phosphates, thiophosphates with alkaline or alkaline earth metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • 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
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4806Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Water Supply & Treatment (AREA)
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  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)
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Abstract

The present invention provides a kind of preparation methods of the hollow Porous HAP microballoon composite material of CdS/ characterized by comprising by CaCl2Solution is added in kayexalate solution, and Na is added dropwise in stirring2CO3Solution stirs to get white suspension, is centrifuged, and cleans, dry, obtains CaCO3Microballoon presoma;By CaCO3Microballoon forerunner dispersion liquid and Na2HPO4Solution mixing, adjusting pH are 10.5-11.5, are reacted, are cooled to room temperature at 110-130 DEG C, are centrifuged, and are cleaned, dry, obtain hollow Porous HAP microballoon;It is mixed after taking CdS and hollow Porous HAP microballoon to be dissolved in deionized water respectively, carries out hydro-thermal reaction, obtain the hollow Porous HAP microballoon composite material of CdS/.The present invention has the degradation property simple, quickly and efficiently for removing tetracycline wastewater.

Description

A kind of hollow Porous HAP microballoon composite material of CdS/ and its preparation and application
Technical field
The invention belongs to materialogy fields, are related to a kind of composite material, specifically a kind of high efficiency photocatalysis degradation four The preparation method of the hollow Porous HAP microballoon composite material of the CdS/ of ring element waste water.
Background technique
As the further understanding and concern, the demand to environment remediation technology of people's environmental pollution also increasingly increase. More especially be similar to the broad-spectrum antibiotics of quadracycline (TC) etc., due to being widely used caused by environmental pollution ask Topic.These antibiotic, which are not only polluted caused by lake, river and ocean, to be got worse, but also is also resulted in the ecosystem various Adverse effect, makes the healthy living of the mankind face grave danger.Therefore, the task of top priority be find it is a kind of green, it is sustainable Method solve the problems, such as that antibiotic pollutes in water environment.Photocatalysis technology have the characteristics that efficiently, environmental protection, it is cheap, be It is a kind of not only to have economized on resources but also environmental-friendly " green " method, thus people is more and more obtained in terms of antibiotic waste water processing Favor.It is well known that the carrier of photocatalysis technology functionization is photochemical catalyst, so design and research and development high-performance optical catalysis Agent is the core missions of photocatalytic degradation antibiotic waste water.But the photochemical catalyst currently used for photocatalytic degradation antibiotic waste water is general Store-through is the removal rate of antibiotic is undesirable, mineralization rate is relatively low, photocatalyst activity and stability is poor and photochemical catalyst Research and develop the defects of on the high side.In addition, compared with other water pollutants such as dyestuff, the more difficult light degradation of antibiotic.Therefore, it actively seeks Summation exploitation has efficiently and the photocatalysis new material and its new preparation process and new technology of high stability are always researchers It is insistent to pursue a goal.
In recent years, hydroxyapatite (Ca10(PO4)6(OH)2, HAP) and it is used as a kind of inorganic functional material, because it has well Biocompatibility, bioactivity, nontoxicity, the environmental-friendly and characteristics such as cheap and be widely used in biomaterial In.In addition, HAP has caused researchers' simultaneously also with excellent organic matter absorption and photocatalytic degradation capability Great interest becomes one of the research hotspot of novel photocatalysis material.
Summary of the invention
It is an object of the present invention to provide materials and its system that a kind of pair of tetracycline wastewater has preferable Photocatalytic Degradation Property Standby and application.
In order to achieve the above object, the present invention provides a kind of preparation sides of the hollow Porous HAP microballoon composite material of CdS/ Method characterized by comprising
Step 1: by CaCl2Solution is added in kayexalate (PSS) solution, and Na is added dropwise in stirring2CO3It is molten Liquid stirs to get white suspension, and obtained solid is used deionized water and washes of absolute alcohol by centrifugation respectively, dry, obtains CaCO3Microballoon presoma;
Step 2: preparing CaCO3Microballoon forerunner's dispersion liquid, by CaCO3Microballoon forerunner dispersion liquid and Na2HPO4Solution is mixed It closes, adjusting pH with NaOH is 10.5-11.5, is reacted, is cooled to room temperature at 110-130 DEG C, is centrifuged, with deionized water and nothing Water-ethanol cleaning, it is dry, obtain hollow Porous HAP microballoon;
Step 3: it is mixed after taking CdS and hollow Porous HAP microballoon to be dissolved in deionized water respectively, carries out hydro-thermal reaction, it is cooling To room temperature, centrifugation is dry by obtained solid, obtains the hollow Porous HAP microballoon composite material of CdS/.
Preferably, the CaCl2The concentration of solution is 0.15M-0.25M.
Preferably, the concentration of the kayexalate (PSS) solution is 5mg/mL-15mg/mL.
Preferably, the Na2CO3The concentration of solution is 0.15M-0.25M.
Preferably, the CaCO3The solid content of microballoon forerunner's dispersion liquid is 5g/L-10g/L.
Preferably, the Na2HPO4The concentration of solution is 0.02M-0.06M.
Preferably, the CaCl2Solution, kayexalate solution and Na2CO3The volume ratio of solution is 1:9-11: 0.9-1.1。
Preferably, the CaCO3And Na2HPO4Molar ratio be 1:0.55-0.65.
Preferably, the weight ratio of the CdS and hollow Porous HAP microballoon is 1:9.5-10.5.
Preferably, the temperature of the hydro-thermal reaction in the step 3 is 75-85 DEG C.
The present invention also provides the hollow Porous HAP microballoon composite materials of CdS/ prepared by above-mentioned preparation method.
The present invention also provides the application methods of the hollow Porous HAP microballoon composite material of above-mentioned CdS/, which is characterized in that It include: that the above-mentioned hollow Porous HAP microballoon composite material of CdS/ is placed in tetracycline, dark reaction reaches absorption- Desorption equilibrium, illumination degrade to tetracycline.
The present invention uses hollow calcium carbonate (CaCO3) microballoon is template and prepares object in conjunction with hydro-thermal method.Using low Warm water thermal method synthesizes CdS/ hollow porous micro sphere HAP composite material.The system of photochemical catalyst with specific composition and appearance structure It is standby to play a key effect to raising photocatalysis performance.Hollow Porous HAP microballoon both can be used as a kind of good adsorbent, can also Using the photochemical catalyst excellent as one kind.Porous characteristic means that light-catalyzed reaction can occur on bigger surface, and The band structure of hollow Porous HAP microballoon can by it is subsequent it is CdS-loaded composite photo-catalyst obtained with this realize adjustment, into And reach higher photocatalysis efficiency.So far, there is not yet the CdS/ for photocatalytic degradation tetracycline wastewater is hollow more Hole HAP microballoon composite material and preparation method thereof patent of invention report.
Compared with prior art, the beneficial effects of the present invention are:
Preparation method of the present invention is scientific, rationally easy, low in cost, repeated height, the resulting hollow Porous HAP of CdS/ are micro- Ball composite material has simple, removal tetracycline wastewater quickly and efficiently degradation property, thus before there is potential application Scape.
Detailed description of the invention
Hollow Porous HAP microballoon scanning electron microscope (SEM) photo of Fig. 1
Fig. 2 CdS (10wt.%)/hollow Porous HAP microballoon composite material X-ray powder diffraction (XRD) diagram
Fig. 3 CdS (10wt.%)/hollow Porous HAP microballoon composite material scanning electron microscope (SEM) diagram
Fig. 4 CdS (10wt.%)/hollow Porous HAP microballoon composite material UV-Vis DRS map (UV-vis) figure Show
Fig. 5 CdS (10wt.%)/hollow Porous HAP microballoon composite material is bent to absorption-photocatalysis performance of tetracycline Line.
Specific embodiment
Present invention will be further explained below with reference to specific examples.It should be understood that these embodiments are merely to illustrate the present invention Rather than it limits the scope of the invention.In addition, it should also be understood that, after reading the content taught by the present invention, those skilled in the art Member can make various changes or modifications the present invention, and such equivalent forms equally fall within the application the appended claims and limited Range.
Used each raw material is commercial product in following embodiment.Polystyrolsulfon acid used in following embodiment Sodium is bought in Guangdong Weng Jiang chemical reagent Co., Ltd (CAS NO.:25704-18-1)
The preparation of the hollow Porous HAP microballoon of embodiment 1:
Configure 50mL0.2M CaCl2Solution and 500mL10mg/mL PSS (kayexalate) solution, then by chlorine Change calcium solution to be added in kayexalate solution, magnetic agitation sufficiently dissolves, then by 50mL 0.2M Na2CO3It is added dropwise Above-mentioned solution, stirs 1h at room temperature, obtains white suspension, and obtained solid is used deionized water and dehydrated alcohol by centrifugation respectively Three times, finally drying for 24 hours, obtains CaCO at 60 DEG C for cleaning3Microballoon presoma.
By the resulting CaCO of 0.2g3Microballoon presoma is scattered in 30mL deionized water, obtains CaCO3Microballoon presoma point Dispersion liquid, by CaCO3The Na that microballoon forerunner dispersion liquid and concentration are 0.04M2HPO4Solution mixes (Ca:P=according to a certain percentage 1.67) it mixes, then with NaOH adjusting pH to 11, in the reaction kettle for stirring evenly and being transferred to polytetrafluoroethyllining lining, 120 DEG C React 1h, be cooled to room temperature, be centrifuged, three times by obtained solid deionized water and washes of absolute alcohol, at 60 DEG C it is dry for 24 hours To hollow Porous HAP microballoon.
Fig. 1 is the hollow Porous HAP microballoon scanning electron microscope (SEM) photograph (SEM) that present example 1 is prepared.It can be seen that made Standby obtained HAP has hollow porous micro sphere structure, and Microsphere Size is about at 1.5 μm or so.
The preparation of 2 CdS of embodiment (10wt.%)/hollow Porous HAP microballoon composite material:
The hollow Porous HAP microballoon and 0.02g CdS that take 0.2g embodiment 1 to prepare are dissolved in the deionized water of 15mL respectively In, ultrasound is uniformly mixed after 1 hour, is transferred in the reaction kettle of polytetrafluoroethyllining lining, 80 DEG C of progress hydro-thermal reaction 4h, cooling To room temperature, centrifugation, by obtained solid deionized water and washes of absolute alcohol, at 60 DEG C it is dry for 24 hours, obtain CdS (10wt.%)/hollow Porous HAP microballoon composite material.
Fig. 2 is that 2 preparation-obtained CdS (10wt.%) of present example/hollow Porous HAP microballoon composite material X is penetrated Line powder diffraction (XRD) spectrogram.As seen from the figure, CdS (10wt.%)/hollow Porous HAP microballoon composite material XRD spectra is The superposition of CdS characteristic absorption peak and HAP characteristic absorption peak, and there is no the appearance of other impurity peaks in composite material, show to close At CdS (10wt.%)/hollow Porous HAP microballoon composite material purity it is higher.
Fig. 3 is that 2 preparation-obtained CdS (10wt.%) of present example/hollow Porous HAP microballoon composite material is swept Retouch Electronic Speculum (SEM) diagram, it can be seen that little particle CdS is carried on the surface of hollow Porous HAP microballoon.
Fig. 4 is 2 preparation-obtained CdS (10wt.%) of present example/hollow Porous HAP microballoon composite material purple Outside-visible diffusing reflection spectrum (UV-Vis DRS) figure, it can be seen that the composite material has superior Uv and visible light to absorb Performance, can be used as photochemical catalyst come using.
3 absorption of embodiment-photocatalysis performance experiment:
Weigh the Fourth Ring that 0.05g CdS (10wt.%)/hollow Porous HAP microballoon composite material is placed in 100mL, 50mg/L In plain (TC) solution, dark reaction 40min is to reach adsorption-desorption balance;Use the luxuriant and rich with fragrance Lay 300WXe xenon lamp of pool for light source, simulation is too Sunlight irradiation, illumination at interval of 5min take the sample of 4mL to be centrifuged, supernatant are placed in cuvette after starting, and utilize Shimadzu UV-2550 ultraviolet specrophotometer measures the absorption value of tetracycline, using C/C0Evaluate degradation rate, wherein C is illumination The concentration of the tetracycline of sample after a certain period of time, C0For the concentration of the initial tetracycline of sample.
Fig. 5 is 3 preparation-obtained CdS (10wt.%) of present example/hollow Porous HAP microballoon composite material to four Absorption-photocatalysis performance curve of ring element, the experimental results showed that it has photocatalytic degradation tetracycline very quickly and efficiently Performance, the tetracycline removal rate for being 50mg/L to initial concentration in 30min is 90.2%, reaches simple, effective, economical, fast The effect of the removal tetracycline wastewater of speed, can be applied to environment protection field.

Claims (10)

1. a kind of preparation method of the hollow Porous HAP microballoon composite material of CdS/ characterized by comprising
Step 1: by CaCl2Solution is added in kayexalate solution, and Na is added dropwise in stirring2CO3Solution stirs to get White suspension, centrifugation, uses deionized water and washes of absolute alcohol for obtained solid respectively, dry, obtains CaCO3Microballoon forerunner Body;
Step 2: preparing CaCO3Microballoon forerunner's dispersion liquid, by CaCO3Microballoon forerunner dispersion liquid and Na2HPO4Solution mixing, is used It is 10.5-11.5 that NaOH, which adjusts pH, is reacted, is cooled to room temperature at 110-130 DEG C, is centrifuged, with deionized water and anhydrous second Alcohol cleaning, it is dry, obtain hollow Porous HAP microballoon;
Step 3: being mixed after taking CdS and hollow Porous HAP microballoon to be dissolved in deionized water respectively, carry out hydro-thermal reaction, be cooled to room Temperature, centrifugation is dry by obtained solid, obtains the hollow Porous HAP microballoon composite material of CdS/.
2. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described CaCl2The concentration of solution is 0.15M-0.25M.
3. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described Kayexalate solution concentration be 5mg/mL-15mg/mL.
4. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described Na2CO3The concentration of solution is 0.15M-0.25M.
5. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described CaCO3The solid content of microballoon forerunner's dispersion liquid is 5g/L-10g/L.
6. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described CaCO3And Na2HPO4Molar ratio be 1:0.55-0.65.
7. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described CdS and hollow Porous HAP microballoon weight ratio be 1:9.5-10.5.
8. the preparation method of the hollow Porous HAP microballoon composite material of CdS/ as described in claim 1, which is characterized in that described Step 3 in hydro-thermal reaction temperature be 75-85 DEG C.
9. the hollow Porous HAP microballoon composite material of CdS/ prepared by preparation method of any of claims 1-8.
10. the application method of the hollow Porous HAP microballoon composite material of CdS/ as claimed in claim 9 characterized by comprising The hollow Porous HAP microballoon composite material of CdS/ as claimed in claim 9 is placed in tetracycline, dark reaction reaches suction Attached-desorption equilibrium, illumination degrade to tetracycline.
CN201910308260.8A 2019-04-17 2019-04-17 A kind of hollow Porous HAP microballoon composite material of CdS/ and its preparation and application Pending CN109985645A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111514853A (en) * 2020-04-30 2020-08-11 合肥学院 Preparation method of calcium carbonate-waste coal-based activated carbon composite adsorbent
CN111672453A (en) * 2020-06-12 2020-09-18 兰州大学 High-value resource utilization method for pig bones
CN112125290A (en) * 2020-09-15 2020-12-25 上海摩漾生物科技有限公司 Calcium-phosphorus microsphere material containing defect sites and preparation and application thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108786889A (en) * 2018-06-21 2018-11-13 上海电力学院 A kind of preparation method of the composite material of efficient absorption-photocatalytic degradation antibiotic

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108786889A (en) * 2018-06-21 2018-11-13 上海电力学院 A kind of preparation method of the composite material of efficient absorption-photocatalytic degradation antibiotic

Non-Patent Citations (1)

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盖莹: "光催化剂HA/TiO2复合材料的制备与性能研究", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111514853A (en) * 2020-04-30 2020-08-11 合肥学院 Preparation method of calcium carbonate-waste coal-based activated carbon composite adsorbent
CN111514853B (en) * 2020-04-30 2022-08-26 合肥学院 Preparation method of calcium carbonate-waste coal-based activated carbon composite adsorbent
CN111672453A (en) * 2020-06-12 2020-09-18 兰州大学 High-value resource utilization method for pig bones
CN111672453B (en) * 2020-06-12 2022-05-06 兰州大学 High-value resource utilization method for pig bones
CN112125290A (en) * 2020-09-15 2020-12-25 上海摩漾生物科技有限公司 Calcium-phosphorus microsphere material containing defect sites and preparation and application thereof

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