CN106669590A - Heavy metal mesoporous adsorbent material with molybdenum ore tailings as raw material as well as preparation method and application thereof - Google Patents

Heavy metal mesoporous adsorbent material with molybdenum ore tailings as raw material as well as preparation method and application thereof Download PDF

Info

Publication number
CN106669590A
CN106669590A CN201611260580.3A CN201611260580A CN106669590A CN 106669590 A CN106669590 A CN 106669590A CN 201611260580 A CN201611260580 A CN 201611260580A CN 106669590 A CN106669590 A CN 106669590A
Authority
CN
China
Prior art keywords
heavy metal
molybdenum ore
ore tailings
raw material
preparation
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
CN201611260580.3A
Other languages
Chinese (zh)
Other versions
CN106669590B (en
Inventor
胡峥
王进进
李永涛
张振
张玉龙
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.)
South China Agricultural University
Original Assignee
South China 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 South China Agricultural University filed Critical South China Agricultural University
Priority to CN201611260580.3A priority Critical patent/CN106669590B/en
Publication of CN106669590A publication Critical patent/CN106669590A/en
Application granted granted Critical
Publication of CN106669590B publication Critical patent/CN106669590B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/103Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
    • 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
    • B01J20/041Oxides or hydroxides
    • 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
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (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)

Abstract

The invention belongs to the technical field of heavy metal pollution treatment for environment and discloses a heavy metal mesoporous adsorbent material with molybdenum ore tailings as raw material as well as a preparation method and an application thereof. The preparation method comprises steps as follows: an alkaline sodium compound is added after molybdenum ore tailings are subjected to acid pickling, the mixture is heated in a muffle furnace and dissolved in water, sodium metaaluminate and water glass are added to a supernatant, the mixture is uniformly mixed and transferred to a reactor to react, an obtained reaction liquid is purified after the reaction ends, and the heavy metal mesoporous adsorbent material is obtained. The mesoporous adsorbent material prepared with the method has a very good adsorption effect on heavy metals, has the removal rate of 95% or above even under the condition that the concentration of heavy metal solutions is up to 420 mg*L<-1>, is stable at adsorption, has no secondary pollution risk and can be applied to heavy metal wastewater treatment. Besides, the characteristics of the raw material, namely, molybdenum ore tailing waste, is fully utilized, waste is treated by waste while the product quality is improved, the preparation process is simple, and industrial production promotion is facilitated.

Description

It is a kind of based on molybdenum ore tailings for raw material heavy metal mesoporous adsorption material and its preparation method and Using
Technical field
The invention belongs to Heavy-Metal-Contaminated Environments processing technology field, more particularly to a kind of is raw material based on molybdenum ore tailings Heavy metal mesoporous adsorption material and its preparation method and application.
Background technology
With the increasingly shortage of water resource, craving of the mankind to water resource is more and more stronger, but water pollution problem Increasingly severe, this causes available water resource less.Therefore the problem for the treatment of pollutant effluents already turns into worldwide asking Topic.Particularly in developing country, the environmental problem of a large amount of discharges of pollutant effluents, or even the barrier for advancing as country and developing Hinder.The features such as heavy metal pollution has toxicity, not biodegradable and accumulation property, is present in water body environment and seriously threatens people Health and life.What National Bureau of Statistics of the People's Republic of China write《China Statistical Yearbook》In mention China in 2014 Discharge of wastewater has reached surprising 71,617,510,000 tons.
Heavy metal classes pollutant once enters water body, is merely able to by changing form or being transferred, dilute, accumulate, and Can not be degraded, even and if the pollution of very low concentrations also can do harm to huamn body.Cadmium, is wherein the one of heavy metal element Kind, it is a kind of very big soft metal of toxicity, it is not belonging to needed by human body element.Its most compound all have it is water-soluble, And with toxicity, therefore once enter water body, it is easy to unconsciously entering food chain, and enrichment, prestige in human body Coerce human health.Cadmium is enriched in liver, pancreas, stomach and thyroid gland into people's cognition, and kidney can be made to produce irreversible disease Become, cause osteoporosis, angiocardiopathy, nervous system and immune system are damaged.China《Integrated wastewater discharge mark It is accurate》And《Drinking Water hygienic quality specification》The concentration limit of the cadmium of middle clear stipulaties is respectively 0.1ppm and 5ppb.
The main source of heavy metal wastewater thereby includes chemical industry, the opening of Pb-Zn deposits, electroplating industry, non-ferrous metal metallurgy, system The discharge of the waste water such as standby sulfuric acid industry, printing and dyeing textile, pesticide producing.
The method of heavy metal containing wastewater treatment can substantially be divided into physical treatment process, chemical method, biological treatment three major types.Its Middle chemical method mainly includes the precipitation method and electrolysis;Physical treatment process includes solvent extraction and separation method, ion-exchange, film point From and absorption method;Biological treatment includes biosorption process, bio-flocculation process, phytoremediation.
Absorption method is a kind of effective ways of heavy metal ion in the material Adsorption water for utilize cellular structure, is mesh One of method of pre-treatment industrial waste water containing Cd.The key technology of absorption method is the selection of adsorbent, common sorbing material bag Include zeolite, activated carbon etc..Activated carbon has very strong adsorption capacity, and clearance is high, but regenerating active carbon efficiency is low, and water quality treatment is difficult Reach reuse requirement, price, using being restricted.Zeolite is natural sorbing material, and specific surface area is big, with very strong suction Attached ability, is most already applied to the handling process of heavy metal wastewater thereby.In recent years, various suctions of adsorption capacity are gradually developed Enclosure material.
Utilization rate of the mineral resources when developing be not substantially high, and useful constituent only accounts for small part, most thing Matter will be as mine tailing.So resource of tailings is all constantly being accumulated every year, a large amount of CHARACTERISTICS OF TAILINGS SANDs are deposited in Tailings Dam, do not only take up soil Ground, waste of resource, and there is the environmental risk of pollution.
CHARACTERISTICS OF TAILINGS SAND as trade waste one kind, be a kind of resource for mislaying, current its treatment approach has three Kind.The first is that, with the continuous progress of science and technology, the tailings of fraction can extract useful mineral resources by selecting again; Second is as building materials, light industry, Inorganic Chemicals, production such as devitrified glass, architectural pottery, building brick;Last Plant is, as dispensing, to participate in portland cement, synthesis of mineral material etc..
The content of the invention
In order to overcome the shortcomings and deficiencies of the prior art described above, primary and foremost purpose of the invention is to provide a kind of based on molybdenum ore Tailings is the preparation method of the heavy metal mesoporous adsorption material of raw material.
Another object of the present invention is offer above method preparation based on the mesoporous suction of heavy metal that molybdenum ore tailings is raw material Enclosure material.
Still a further object of the present invention is that offer is above-mentioned to be weighed based on the heavy metal mesoporous adsorption material that molybdenum ore tailings is raw material The application of metallic wastewater treatment.
The purpose of the present invention is realized by following proposal:
A kind of is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, specifically includes following step Suddenly:
(1) milled 200 mesh sieve of molybdenum ore tailings, adds dilute acid soln to be vibrated in shaking table, is separated by filtration, and dries, then It is sub-packed in crucible, each crucible adds alkaline sodium compound, then the heat altogether in Muffle furnace, then takes out natural cooling, grinds It is stand-by.
Dilute acid soln described in step (1) can be dilute sulfuric acid aqueous solution or diluted hydrochloric acid aqueous solution, the concentration of dilute acid soln Preferably 1mol/L;The consumption of dilute acid soln used remains to be totally submerged molybdenum ore tailings with the dilute acid soln under oscillating condition It is accurate.
Vibration described in step (1) refers to the 240rmin in horizontal reciprocating oscillator-112h is vibrated under speed.
Alkaline sodium compound described in step (1) can be sodium carbonate or NaOH, preferably NaOH.
In crucible described in step (1) dry after molybdenum ore tailings and alkaline sodium compound mass ratio for (0.6~ 1):1。
The common heat in Muffle furnace described in step (1) refers in 1~3h of the common heat of 573K~973K.
Described in step (1) grind it is stand-by in the purpose that grinds be more thorough in order to what is dissolved in water.
(2) take step (1) product to be dissolved in water, centrifugal filtration takes supernatant, is transferred in teflon tanks, and adds inclined aluminium Sour sodium and waterglass control material ratio, fully mix under magnetic agitation;
Addition sodium metaaluminate and waterglass control material described in step (2) is than being that the mol ratio for instigating reaction mass is (5.5~7.5) Na2O:Al2O3:2.88SiO2:212.4H2O;
Mixing described in step (2) refers to 1~3h of mixing under 333~373K water bath conditions.
(3) reaction mass after being mixed in teflon tanks is transferred in reactor, reactor is put into Muffle furnace or baking Reacted in case, reaction terminate after take out be cooled to room temperature, filter, washing, dry, obtained powder solid be sodium form with much money Category mesoporous adsorption material.
The volume of the reaction mass after being mixed in the teflon tanks described in step (3) is the 2/3 of reactor volume.
Reaction described in step (3) refers to 8~36h of reaction under the conditions of 353~473K.
Washing described in step (3) refers to use 0.01molL-1The NaOH aqueous solution is washed.
It is a kind of by above-mentioned reaction prepare based on molybdenum ore tailings for raw material heavy metal mesoporous adsorption material.
The above-mentioned application based on the heavy metal mesoporous adsorption material that molybdenum ore tailings is raw material in heavy metal containing wastewater treatment.
Mechanism of the invention is:
Mineral wherein active constituent content ore high in ore dressing process is chosen away, and remaining mine tailing main component is two Silica, alundum (Al2O3).Silica, alundum (Al2O3) are as the main constituents in the earth's crust it is necessary to fabulous environment Compatibility.It is raw material present invention utilizes the silica and aluminum oxide in molybdenum ore tailings, is activated by acid-base method, by control The factors such as material ratio processed, basicity, temperature, in the reactor under high pressure synthesis with bigger serface, pore volume aperture it is new Mineral, make it on the premise of its outstanding environment compatibility is kept, with the characteristic for adsorbing pollutant.
The present invention has the following advantages and beneficial effect relative to prior art:
(1) adsorption effect of mesoporous adsorption material heavy metal prepared by the present invention is very good, even if in heavy metal solution At concentrations up to 420mgL-1Under, still there is stabilization after more than 95% clearance, and absorption, there is no secondary pollution risk.
(2) primary raw material of mesoporous adsorption material is tailings, using a kind of waste material, realizes the mesh of the treatment of wastes with processes of wastes against one another 's.
(3) characteristic of former molybdenum ore tailings discarded object is made full use of, the quality of product is improved.There is good aluminium in molybdenum ore tailings Matter and siliceous source, and contain a small amount of K2O、Na2O, beneficial to the stabilization of mesoporous material under alkalescence condition.
(4) preparation process is simple, promotes beneficial to industrial production.
Brief description of the drawings
Fig. 1 is the clearance of the heavy metal mesoporous adsorption material to Cd in the solution containing Cd of various concentrations of the preparation of embodiment 1 Figure.
Specific embodiment
With reference to embodiment and accompanying drawing, the present invention is described in further detail, but embodiments of the present invention are not limited In this.
Agents useful for same can routinely be bought from market unless otherwise specified in embodiment.
The molybdenum ore tailings used in example comes from Guangdong Province Meizhou Wuhua, and its main chemical compositions (wt%) is:
Molybdenum ore tailings component SiO2 Al2O3 Fe2O3 TiO3 Na2O K2O MgO CaO P2O5 CuO
Content 78.35 10.95 1.54 0.46 1.65 3.40 0.42 0.64 0.12 0.01
Embodiment 1:It is the preparation of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings
(1) milled 200 mesh sieve of 15g molybdenum ore tailings is taken, the H of 30ml, 1mol/L is added2SO4Vibrated in shaking table, filtering Separate, drying;It is sub-packed in crucible, the NaOH of the quality such as each crucible addition is warm altogether in the Muffle furnace of 823K, is taken out after 3h Natural cooling, grinds stand-by.
(2) 5g steps (1) are taken and grinds stand-by product plus 90ml deionized water dissolvings, centrifugal filtration takes supernatant, shifted Into teflon tanks, and add 5.4g sodium metaaluminates and 15.75g waterglass regulation material ratio, the magnetic agitation under the conditions of 343K 1h。
(3) reaction mass after being stirred in teflon tanks is transferred in reactor, is reacted under the conditions of 373K, instead Taking-up is cooled to room temperature after answering 8h, filters, and washing is dried, and prepared powder solid is sodium form heavy metal mesoporous adsorption material.
Embodiment 2
With 0.05molL-1Used as supporting electrolyte solution, it is 100mgL to prepare Cd solution concentrations to NaCl solution-1's Heavy metal ion solution.The metal ion solution of the above-mentioned concentration of 25mL is measured, addition fills the heavy metal of the preparation of 0.1g embodiments 1 In the 50mL centrifuge tubes of sorbing material, each treatment is repeated 3 times, and averages.Excellent centrifuge tube will be added to cover, in 250r min-1, vibrate 24h under the conditions of (25 ± 2) DEG C, be then 6000rmin in rotating speed-1Lower centrifugation 30min, filtering, is inhaled with atom Receive the concentration of the Cd ions after AAS (AAS) measure is balanced in solution.
Supernatant C d concentration is 0.25mgL after showing the balance surveyed with the result of sorbing material obtained in NaOH-1, I.e. handling rate is up to 99.76%.
Embodiment 3
With 0.05molL-1NaCl solution is used as supporting electrolyte solution, and the metal ion that following concentration is prepared respectively is molten Liquid, Cd solution concentrations:20、30、60、100、140、190、280、420mg·L-1;The metal ion for measuring the above-mentioned concentration of 25mL is molten Liquid, addition is filled in the 50mL centrifuge tubes of the heavy-metal adsorption material of the preparation of 0.1g embodiments 1, and each treatment is repeated 3 times, and makes even Average.Excellent centrifuge tube will be added to cover, in 250rmin-1, vibrate 24h under the conditions of (25 ± 2) DEG C, be then in rotating speed 6000r·min-1Lower centrifugation 30min, filtering determines the Cd ions in solution after balancing with atomic absorption spectrophotometry (AAS) Concentration, so as to draw clearance.
Clearance figure of the heavy-metal adsorption material prepared in embodiment 1 to Cd in the solution containing Cd under various concentrations As shown in figure 1, being as can be seen from Figure 1 less than 420mgL in Cd concentration-1When, the heavy metal that embodiment 1 is prepared is mesoporous Sorbing material has all reached more than 98.5% to the clearance of Cd, and preceding 7 concentration (20,30,60,100,140,190, 280mg·L-1) handling rate all reached more than 99.6%, illustrate the present invention preparation sodium form heavy metal mesoporous adsorption material pair Cd has preferable adsorption effect.
Embodiment 4
In order to probe into heavy metal mesoporous material that embodiment 1 prepares after Adsorption of Heavy Metals, risk in the environment. Simulated Acid Rain solution is configured according to condition elements such as In Guangzhou Area acid rain constituent, pH value for many years, after Adsorption of Heavy Metals Material carry out desorption experiment.
Configuration S/N compositions ratio (mass ratio) is 3: 1, and pH value is 3.5 Simulated Acid Rain solution.In taking 25mL and embodiment 3 Cd concentration is 280mgL-1、420mg·L-1Residue mixing (solid-to-liquid ratio 1g after lower absorption:250mL), in 250rmin-1、 24h is vibrated under the conditions of (25 ± 2) DEG C, is then 6000rmin in rotating speed-1Lower centrifugation 30min, filtering, uses atomic absorption spectrophotometry Photometry (AAS) determines the concentration of the Cd ions in solution after balancing.
Result shows, is 280mgL in Cd concentration-1Residue desorption efficiency after lower absorption is 0.06%, is in Cd concentration 420mg·L-1Residue desorption efficiency is 0.07% after lower absorption.Therefore, material will not be deposited substantially after high concentration heavy metal is adsorbed Desorbing the possibility that causes secondary pollution.
Above-described embodiment is the present invention preferably implementation method, but embodiments of the present invention are not by above-described embodiment Limitation, it is other it is any without departing from Spirit Essence of the invention and the change, modification, replacement made under principle, combine, simplification, Equivalent substitute mode is should be, is included within protection scope of the present invention.

Claims (8)

1. a kind of is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, it is characterised in that specifically included Following steps:
(1) milled 200 mesh sieve of molybdenum ore tailings, adds dilute acid soln to be vibrated in shaking table, is separated by filtration, and dries, and then dispenses In crucible, each crucible adds alkaline sodium compound, then the heat altogether in Muffle furnace, then takes out natural cooling, grinds stand-by;
(2) take step (1) product to be dissolved in water, centrifugal filtration takes supernatant, is transferred in teflon tanks, and add sodium metaaluminate With waterglass control material ratio, fully mixed under magnetic agitation;
(3) reaction mass after being mixed in teflon tanks is transferred in reactor, during reactor is put into Muffle furnace or baking oven Reacted, reaction is taken out after terminating and is cooled to room temperature, is filtered, washing is dried, and obtained powder solid is the mesoporous suction of heavy metal Enclosure material.
2. according to claim 1 is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, its It is characterised by:
Dilute acid soln described in step (1) is dilute sulfuric acid aqueous solution or diluted hydrochloric acid aqueous solution, and the concentration of dilute acid soln is 1mol/ L;The consumption of dilute acid soln used is remained to be totally submerged molybdenum ore tailings and is defined by the dilute acid soln under oscillating condition;
Vibration described in step (1) refers to the 240rmin in horizontal reciprocating oscillator-112h is vibrated under speed.
3. according to claim 1 is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, its It is characterised by:
Alkaline sodium compound described in step (1) is sodium carbonate or NaOH;
The mass ratio of molybdenum ore tailings and alkaline sodium compound after being dried in the crucible described in step (1) is (0.6~1):1;
The common heat in Muffle furnace described in step (1) refers in 1~3h of the common heat of 573K~973K.
4. according to claim 3 is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, its It is characterised by:
Alkaline sodium compound described in step (1) is NaOH.
5. according to claim 1 is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, its It is characterised by:
Addition sodium metaaluminate and waterglass control material described in step (2) are than being that to instigate the mol ratio of reaction mass be (5.5 ~7.5) Na2O:Al2O3:2.88SiO2:212.4H2O;
Mixing described in step (2) refers to 1~3h of mixing under 333~373K water bath conditions.
6. according to claim 1 is the preparation method of the heavy metal mesoporous adsorption material of raw material based on molybdenum ore tailings, its It is characterised by:
The volume of the reaction mass after being mixed in the teflon tanks described in step (3) is the 2/3 of reactor volume;
Reaction described in step (3) refers to 8~36h of reaction under the conditions of 353~473K;
Washing described in step (3) refers to use 0.01molL-1The NaOH aqueous solution is washed.
7. what a kind of method according to any one of claim 1~6 was prepared is a huge sum of money for raw material based on molybdenum ore tailings Category mesoporous adsorption material.
8. it is according to claim 7 based on molybdenum ore tailings for raw material heavy metal mesoporous adsorption material at heavy metal wastewater thereby Application in reason.
CN201611260580.3A 2016-12-30 2016-12-30 It is a kind of based on the heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material Active CN106669590B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611260580.3A CN106669590B (en) 2016-12-30 2016-12-30 It is a kind of based on the heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611260580.3A CN106669590B (en) 2016-12-30 2016-12-30 It is a kind of based on the heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material

Publications (2)

Publication Number Publication Date
CN106669590A true CN106669590A (en) 2017-05-17
CN106669590B CN106669590B (en) 2019-05-07

Family

ID=58872658

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611260580.3A Active CN106669590B (en) 2016-12-30 2016-12-30 It is a kind of based on the heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material

Country Status (1)

Country Link
CN (1) CN106669590B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108083409A (en) * 2017-12-27 2018-05-29 盐城工学院 A kind of waste water treating agent and preparation method thereof
CN108355607A (en) * 2018-02-09 2018-08-03 长江水利委员会长江科学院 It is a kind of to utilize the functional material for selecting copper tailings to prepare and its preparation process
CN112892470A (en) * 2021-01-19 2021-06-04 华南农业大学 Ferrite-embedded zeolite material, preparation method thereof and application thereof in heavy metal treatment

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101723397A (en) * 2009-11-27 2010-06-09 抚顺矿业集团有限责任公司 Method for preparing zeolite molecular sieve by using oil shale residues
CN102259888A (en) * 2011-05-05 2011-11-30 青岛惠城石化科技有限公司 Method for synthesizing Y-shaped molecular sieve
CN104437354A (en) * 2014-12-01 2015-03-25 浙江大学 Method for preparing improved coal ash-zeolite composite particles
CN106215857A (en) * 2016-09-08 2016-12-14 天津大学 A kind of modified coal slag adsorbent and preparation method and application

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101723397A (en) * 2009-11-27 2010-06-09 抚顺矿业集团有限责任公司 Method for preparing zeolite molecular sieve by using oil shale residues
CN102259888A (en) * 2011-05-05 2011-11-30 青岛惠城石化科技有限公司 Method for synthesizing Y-shaped molecular sieve
CN104437354A (en) * 2014-12-01 2015-03-25 浙江大学 Method for preparing improved coal ash-zeolite composite particles
CN106215857A (en) * 2016-09-08 2016-12-14 天津大学 A kind of modified coal slag adsorbent and preparation method and application

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
DONGYANG MA ET AL: "Feasible conversion of solid waste bauxite tailings into highly crystalline 4A zeolite with valuable application", 《WASTE MANAGEMENT》 *
PENG-CHENG LEI ET AL: "An improved implementable process for the synthesis of zeolite 4A from bauxite tailings and its Cr3+ removal capacity", 《INTERNATIONAL JOURNAL OF MINERALS, METALLURGY AND MATERIALS》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108083409A (en) * 2017-12-27 2018-05-29 盐城工学院 A kind of waste water treating agent and preparation method thereof
CN108355607A (en) * 2018-02-09 2018-08-03 长江水利委员会长江科学院 It is a kind of to utilize the functional material for selecting copper tailings to prepare and its preparation process
CN108355607B (en) * 2018-02-09 2020-10-27 长江水利委员会长江科学院 Functional material prepared by using copper-selecting tailings and preparation process thereof
CN112892470A (en) * 2021-01-19 2021-06-04 华南农业大学 Ferrite-embedded zeolite material, preparation method thereof and application thereof in heavy metal treatment

Also Published As

Publication number Publication date
CN106669590B (en) 2019-05-07

Similar Documents

Publication Publication Date Title
Papadopoulos et al. Nickel uptake from a wastewater stream produced in a metal finishing industry by combination of ion-exchange and precipitation methods
CN102489245B (en) Modified pumice absorbing material and preparation method as well as application thereof
CN103706326B (en) A kind of preparation method of natural minerals loaded nano defluorinating agent
CN101982580B (en) Polyacrylonitrile/hydroxyapatite composite adsorbent fiber and preparation method thereof
CN103482783A (en) Treatment process for plumbic acid waste water generated in production process of lead storage batteries
CN101549873A (en) Surface active agent modification zeolites, method of preparing thereof and usage
CN103191582B (en) Method for removing bivalent copper ions in aqueous solution
CN104971697A (en) Preparation and application methods for magnetic biochar material used for removing arsenic pollution in water body
CN106669590B (en) It is a kind of based on the heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material
CN108178605A (en) A kind of Preparation method and use of the residual mud baking-free ceramicite of high absorption property water supply plant
CN109261133A (en) A kind of ferromagnetism composite balls and its application being easily recycled
CN105948328A (en) Low-emission purification treatment technology for fluorine-containing waste water based on fluidized-bed crystallization method
CN105233570B (en) A kind of composite modified quartz sand filter media of metal oxide iron copper and its preparation method and application
CN107473321A (en) A kind of permeable reactive barrier active material and preparation method thereof
Hu et al. Phosphorus recovery and resource utilization from phosphogypsum leachate via membrane-triggered adsorption and struvite crystallization approach
Feng et al. Production of sorption functional media (SFM) from clinoptilolite tailings and its performance investigation in a biological aerated filter (BAF) reactor
CN106622115B (en) It is a kind of based on the potassium type heavy metal mesoporous adsorption material and its preparation method and application that molybdenum ore tailings is raw material
CN113952923B (en) Modified micron zeolite and application thereof
CN206645859U (en) A kind of sewage-treatment plant for stirring Joint adsorption
CN102092869A (en) Processing method of waste acid in acid producing system
CN107913663A (en) A kind of method that COD in beneficiation wastewater is removed using flyash
CN209522702U (en) Waste acid treating device for titanium white production
CN107376881A (en) A kind of modification of flyash for treatment of Power waste water and application method
CN112371089A (en) Irregular hexahedron colloidal particle and preparation method and application thereof
CN112844304A (en) Sodium pyrophosphate modified water purification sludge/zeolite composite adsorbent and preparation method 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
GR01 Patent grant
GR01 Patent grant