CN109395700A - A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water - Google Patents

A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water Download PDF

Info

Publication number
CN109395700A
CN109395700A CN201811353808.2A CN201811353808A CN109395700A CN 109395700 A CN109395700 A CN 109395700A CN 201811353808 A CN201811353808 A CN 201811353808A CN 109395700 A CN109395700 A CN 109395700A
Authority
CN
China
Prior art keywords
microalgae
adsorption agent
biological adsorption
compound
magnetic
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201811353808.2A
Other languages
Chinese (zh)
Inventor
高锋
李晨
杨红丽
赵科泉
任鹏炜
朱占军
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.)
Zhejiang Ocean University ZJOU
Original Assignee
Zhejiang Ocean University ZJOU
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 Zhejiang Ocean University ZJOU filed Critical Zhejiang Ocean University ZJOU
Priority to CN201811353808.2A priority Critical patent/CN109395700A/en
Publication of CN109395700A publication Critical patent/CN109395700A/en
Pending legal-status Critical Current

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
    • B01J20/22Solid 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
    • B01J20/02Solid 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
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28009Magnetic properties
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • B01J20/28016Particle form
    • B01J20/28021Hollow particles, e.g. hollow spheres, microspheres or cenospheres
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/322Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
    • 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
    • B01J2220/46Materials comprising a mixture of inorganic and organic materials
    • 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
    • B01J2220/4825Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
    • 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)
  • Engineering & Computer Science (AREA)
  • Biotechnology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Botany (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Inorganic Chemistry (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Preparation Of Compounds By Using Micro-Organisms (AREA)

Abstract

The present invention relates to a kind of methods of cadmium in sewage treatment field more particularly to compound microalgae biological adsorption agent and its adsorbent absorption waste water.It overcomes in the processing of microalgae absorption Pollutants in Wastewater in the prior art, microalgae is easy to be lost from reactor, and the separating difficulty of microalgae and waste water is big after the completion of processing, problem at high cost, activity of microalgae is lower, by chlorella cells elder generation and Fe3O4Nanoparticle carries out absorption connection, then carries out mixing embedding fixation with sodium alginate again, prepares compound microalgae biological adsorption agent, which has many advantages, such as that adsorption capacity is big, the rate of adsorption is fast, simple to operate, and includes magnetic Fe3O4Nanoparticle can facilitate the quick recycling for realizing adsorbent after having handled waste water.The compound microalgae biological adsorption agent is used for the Adsorption of heavy metal ions in wastewater cadmium (Cd), achieves good removal effect.

Description

A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water
Technical field
The present invention relates to sewage treatment fields more particularly to a kind of compound microalgae biological adsorption agent and its adsorbent to adsorb The method of cadmium in waste water.
Background technique
Cadmium (Cd) is widely used in the fields such as electroplating industry, chemical industry, electronics industry and nuclear industry as a kind of metal, every year There are a considerable amount of cadmiums (Cd) to be discharged into environment by exhaust gas, waste water, waste residue, pollutes.Compared to other metals, cadmium is easier It is absorbed by crops, to form huge threat to human health.
Common cadmium (Cd) processing method has the methods of chemical precipitation method, ion-exchange, absorption method.Absorption method is for giving up The removal of heavy metal contaminants is flexible and convenient with operating process in water, is able to achieve advanced treating, recycles waste water by energy of desorption In heavy metal ion the advantages that, be widely used in the processing of all kinds of heavy metal wastewater therebies.
Chlorella as a kind of microalgae have growth rate it is fast, the low advantage of toxigenic capacity, and can effectively adsorb and The some metal ions being enriched in water, are a kind of efficient living body biological adsorbents.It is polluted in traditional microalgae absorption waste water In the processing of object, microalgae is generally in the state of suspension growth, be easy be lost from reactor, and handle after the completion of microalgae with The separation of waste water brings biggish operating cost, and the microalgae of suspension growth is weaker to the resistance of toxicant, in waste water Under the action of the pollutants such as middle heavy metal, activity is often difficult to maintain, and causes whole treatment effeciency lower.
Such as a kind of a kind of method for Immobilized cells culture processing breeding wastewater reported in Chinese patent literature, it is open Number be CN108424906A, with chlorella to the absorption and utilization of nutriment in waste water and other microelements and seaweed The immobilization role of sour sodium makes chlorella can be good at carrying out the separation of algae water while playing catharsis to waste water.We The advantages of method be with Immobilization in Sodium Alginate chlorella handle aquiculture waste water, alleviate increasingly serious fresh water pressure; And absorption and utilization of the chlorella to various elements in waste water, it is purified waste water, and then slow down it and be ultimately discharged into The load of natural water.But there is also shortcomings, such as its recycling is more difficult, needs by constantly filtering It can be realized, the separation of algae water, separating difficulty is larger.
Summary of the invention
The present invention is to overcome in the processing of microalgae absorption Pollutants in Wastewater in the prior art, and microalgae is easy from reaction It is lost in device, the separating difficulty of microalgae and waste water is big after the completion of processing, and problem at high cost, activity of microalgae is lower provides one Kind can effectively fix microalgae, prevent microalgae to be lost from reactor, the convenient separation of microalgae and waste water, micro- after the completion of processing The method of cadmium in a kind of high compound microalgae biological adsorption agent of algae activity and its adsorbent absorption waste water.
For achieving the above object, the invention is realized by the following technical scheme:
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in the medium, medium centrifugal separation obtains lower layer's concentration Microalgae biology;
(S.2) magnetic particle compounds: the microalgae biology dilution of concentration, and and magnetic Fe3O4Nanoparticle is compounded, and is completed micro- Frustule and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: sodium alginate being added in Xiang Shangshu solution, is then added drop-wise to CaCl2In solution, prepare Immobilized microspheres, i.e., compound microalgae biological adsorption agent.
Microalgae biological adsorption agent in the present invention its by by microalgae and Fe3O4Compounded between nanoparticle, by its two Person carries out absorption connection, so that microalgae adsorption has Fe3O4Nanoparticle so that microalgae its have magnetism, then again will It is immobilized, and prepares immobilized microspheres, can prevent the suspension growth of microalgae, solves traditional microalgae absorption waste water In the processing of middle pollutant, microalgae is generally in the state of suspension growth, is easy the problem of being lost from reactor.Meanwhile it passing The microalgae of suspension growth is weaker to the resistance of toxicant in system method, under the action of the pollutants such as heavy metal in waste water, Its activity is often difficult to maintain, and causes whole treatment effeciency lower, its resistance to toxicant after being fixed Effectively enhancing, improves whole treatment effeciency.It, just can be effective by magnetic-adsorption meanwhile after the completion of sewage treatment Promotion is adsorbed, thus effective pair of separation sewage and microalgae.
Preferably, culture medium is BG11 culture medium in the step (S.1), the centrifugation rate is 3000- 5000rpm, centrifugation time 5-10min.
Preferably, being diluted using sterile water to the microalgae biology of concentration in the step (S.2), concentration is adjusted The OD of liquid680For 1-1.5.
As the OD of concentrate680Value is in this interval range, and activity is higher, therefore its suction to heavy metal in sewage Attached performance activity with higher.
Preferably, magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、 FeSO4Acidic iron salt solutions are prepared with hydrochloric acid, make Fe3+、Fe2+Molar ratio with HCl is (1.0-2.5): 1:1, which is dripped It is added in the ammonium hydroxide that mass fraction is 20%-30%, the volume ratio of iron salt solutions and ammonium hydroxide is 1:3-1:5, is stirred evenly, wait produce After object color becomes brown, magnetic separation is staticly settled and carried out, extra liquid is gone, the precipitating of bottom is sucked simultaneously with magnet Distilled water is added to clean 3-4 times, filtering obtains Fe3O4, through 36~72h of vacuum freeze drying, it is prepared into magnetic Fe3O4Nanoparticle Son.
Magnetic Fe in the present invention3O4Nanoparticle passes through Fe3+、Fe2+Between compounding, then will be obtained by ammonia precipitation process To Fe3O4Nanoparticle, with good magnetism, so that can be reduced by magnetic-adsorption after microalgae absorption is fixed The difficulty that microalgae is separated with waste water.
Preferably, magnetic Fe in the step (S.2)3O4The additive amount of nanoparticle is to add magnetic in every liter of algae solution Property Fe3O40.2~0.4g of nanoparticle.
Preferably, compounding condition is isothermal vibration 2-4 days in the step (S.2).
Preferably, the mass fraction concentration of sodium alginate is 5%-7%, CaCl in the step (S.3)2Solution Mass concentration is 3.5%.
Preferably, in the step (S.3), the diameter of immobilized microspheres obtained is 2-5mm, in immobilized microspheres Biomass containing microalgae is 1.0 × 109-6.0×109cell/g。
The diameter of immobilized microspheres in the present invention is smaller, thus the life of specific surface area with higher and higher concentration Object amount, so as to promote the efficiency of pollutant in absorption effluent.
A method of if preceding resulting compound microalgae biological adsorption agent adsorbs cadmium in waste water, the method is as follows: The compound microalgae biological adsorption agent is added in cadmium wastewater, the removal of cadmium in waste water is completed in concussion absorption, after the completion of absorption Quick magnetic separation is carried out to the microalgae biological adsorption agent in waste water.
Compound microalgae biological adsorption agent in the present invention is after having adsorbed the cadmium element in water, it is thus only necessary to pass through magnetic force Separation can separate sewage with compound microalgae biological adsorption agent, have the characteristics that high-efficient simple, to reduce separation Cost.
Preferably, the concentration of cadmium is 2-20mg/L, the throwing of compound microalgae biological adsorption agent in the cadmium wastewater Dosage is 10-25g/L, and adsorption temp is 28-36 DEG C, pH value 6-9.
Therefore, the invention has the following advantages: the compound microalgae biological adsorption agent in (1) present invention can be effective Fixed microalgae, prevents microalgae to be lost from reactor;(2) convenient separation of microalgae and waste water, separation costs are low after the completion of handling; (3) microalgae resistance to poison is stronger, and activity is high, and disposed of in its entirety treatment effeciency is high.
Specific embodiment
The embodiment of technical solution of the present invention will be described in detail below.Following embodiment is only used for clearer Ground illustrates technical solution of the present invention, therefore is only used as an example, and not intended to limit the protection scope of the present invention.
Compound microalgae biological adsorption agent
Embodiment 1
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in BG11 culture medium, culture solution is centrifugated at 4500rpm 7min obtains the microalgae biology of lower layer's concentration;
(S.2) magnetic particle compounds: the microalgae biology of concentration is diluted with sterile water, adjusts the OD of concentrate680It is 1.1, and and magnetic Property Fe3O4Nanoparticle is compounded, and adds magnetic Fe in every liter of algae solution3O4Nanoparticle 0.35g, it is complete after isothermal vibration 2 days At microalgae cell and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: the sodium alginate that mass fraction concentration is 5.5% being added in Xiang Shangshu solution, then drips It is added to the CaCl that mass concentration is 3.5%2In solution, preparing diameter is 4mm, the biomass containing microalgae in immobilized microspheres It is 5.5 × 109The immobilized microspheres of cell/g, i.e., compound microalgae biological adsorption agent.
Magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4And hydrochloric acid Acidic iron salt solutions are prepared, Fe is made3+、Fe2+Molar ratio with HCl is 1.0:1:1, which, which is added drop-wise to mass fraction, is In 20% ammonium hydroxide, the volume ratio of iron salt solutions and ammonium hydroxide is 1:3, is stirred evenly, and after coloured product becomes brown, is staticly settled And magnetic separation is carried out, extra liquid is gone, the precipitating of bottom is sucked with magnet and distilled water is added and cleans 3 times, is filtered Obtain Fe3O4, through vacuum freeze drying 36h, it is prepared into magnetic Fe3O4Nanoparticle.
Embodiment 2
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in BG11 culture medium, culture solution is centrifugated at 3,000 rpm 5min obtains the microalgae biology of lower layer's concentration;
(S.2) magnetic particle compounds: the microalgae biology of concentration is diluted with sterile water, adjusts the OD of concentrate680Be 1, and with magnetism Fe3O4Nanoparticle is compounded, and adds magnetic Fe in every liter of algae solution3O4Nanoparticle 0.2g after isothermal vibration 2 days, is completed micro- Frustule and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: the sodium alginate that mass fraction concentration is 5% being added in Xiang Shangshu solution, is then added dropwise The CaCl for being 3.5% to mass concentration2In solution, preparing diameter is 2mm, and the biomass containing microalgae is in immobilized microspheres 1.0×109The immobilized microspheres of cell/g, i.e., compound microalgae biological adsorption agent.
Magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4And hydrochloric acid Acidic iron salt solutions are prepared, Fe is made3+、Fe2+Molar ratio with HCl is 2.5:1:1, which, which is added drop-wise to mass fraction, is In 30% ammonium hydroxide, the volume ratio of iron salt solutions and ammonium hydroxide is 1:5, is stirred evenly, and after coloured product becomes brown, is staticly settled And magnetic separation is carried out, extra liquid is gone, the precipitating of bottom is sucked with magnet and distilled water is added and cleans 4 times, is filtered Obtain Fe3O4, through vacuum freeze drying 72h, it is prepared into magnetic Fe3O4Nanoparticle.
Embodiment 3
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in BG11 culture medium, culture solution is centrifugated at 5000rpm 10min obtains the microalgae biology of lower layer's concentration;
(S.2) magnetic particle compounds: the microalgae biology of concentration is diluted with sterile water, adjusts the OD of concentrate680It is 1.5, and and magnetic Property Fe3O4Nanoparticle is compounded, and adds magnetic Fe in every liter of algae solution3O4Nanoparticle 0.4g after isothermal vibration 4 days, is completed Microalgae cell and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: the sodium alginate that mass fraction concentration is 7% being added in Xiang Shangshu solution, is then added dropwise The CaCl for being 3.5% to mass concentration2In solution, preparing diameter is 5mm, and the biomass containing microalgae is in immobilized microspheres 6.0×109The immobilized microspheres of cell/g, i.e., compound microalgae biological adsorption agent.
Magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4And hydrochloric acid Acidic iron salt solutions are prepared, Fe is made3+、Fe2+Molar ratio with HCl is 1.5:1:1, which, which is added drop-wise to mass fraction, is In 25% ammonium hydroxide, the volume ratio of iron salt solutions and ammonium hydroxide is 1:4, is stirred evenly, and after coloured product becomes brown, is staticly settled And magnetic separation is carried out, extra liquid is gone, the precipitating of bottom is sucked with magnet and distilled water is added and cleans 3 times, is filtered Obtain Fe3O4, through vacuum freeze drying 60h, it is prepared into magnetic Fe3O4Nanoparticle.
Embodiment 4
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in BG11 culture medium, culture solution is centrifugated at 4000rpm 8min obtains the microalgae biology of lower layer's concentration;
(S.2) magnetic particle compounds: the microalgae biology of concentration is diluted with sterile water, adjusts the OD of concentrate680It is 1.2, and and magnetic Property Fe3O4Nanoparticle is compounded, and adds magnetic Fe in every liter of algae solution3O4Nanoparticle 0.3g after isothermal vibration 3 days, is completed Microalgae cell and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: the sodium alginate that mass fraction concentration is 6% being added in Xiang Shangshu solution, is then added dropwise The CaCl for being 3.5% to mass concentration2In solution, preparing diameter is 3mm, and the biomass containing microalgae is in immobilized microspheres 5.0×109The immobilized microspheres of cell/g, i.e., compound microalgae biological adsorption agent.
Magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4And hydrochloric acid Acidic iron salt solutions are prepared, Fe is made3+、Fe2+Molar ratio with HCl is 2:1:1, and it is 25% which, which is added drop-wise to mass fraction, Ammonium hydroxide in, the volume ratio of iron salt solutions and ammonium hydroxide is 1:4, is stirred evenly, and after coloured product becomes brown, staticly settles and goes forward side by side Row magnetic separation removes extra liquid, and the precipitating of bottom is sucked with magnet and distilled water is added and cleans 4 times, and filtering obtains Fe3O4, through vacuum freeze drying 48h, it is prepared into magnetic Fe3O4Nanoparticle.
Embodiment 5
A kind of compound microalgae biological adsorption agent, the compound microalgae biological adsorption agent the preparation method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in BG11 culture medium, culture solution is centrifugated at 3500rpm 6min obtains the microalgae biology of lower layer's concentration;
(S.2) magnetic particle compounds: the microalgae biology of concentration is diluted with sterile water, adjusts the OD of concentrate680It is 1.3, and and magnetic Property Fe3O4Nanoparticle is compounded, and adds magnetic Fe in every liter of algae solution3O4Nanoparticle 0.35g, it is complete after isothermal vibration 3 days At microalgae cell and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: the sodium alginate that mass fraction concentration is 5%-7% being added in Xiang Shangshu solution, then It is added drop-wise to the CaCl that mass concentration is 3.5%2In solution, preparing diameter is 4mm, the biology containing microalgae in immobilized microspheres Amount is 4.0 × 109The immobilized microspheres of cell/g, i.e., compound microalgae biological adsorption agent.
Magnetic Fe in the step (S.2)3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4And hydrochloric acid Acidic iron salt solutions are prepared, Fe is made3+、Fe2+Molar ratio with HCl is 1.8:1:1, which, which is added drop-wise to mass fraction, is In 28% ammonium hydroxide, the volume ratio of iron salt solutions and ammonium hydroxide is 1:5, is stirred evenly, and after coloured product becomes brown, is staticly settled And magnetic separation is carried out, extra liquid is gone, the precipitating of bottom is sucked with magnet and distilled water is added and cleans 3 times, is filtered Obtain Fe3O4, through vacuum freeze drying 70h, it is prepared into magnetic Fe3O4Nanoparticle.
The method of cadmium in compound microalgae biological adsorption agent absorption waste water
Embodiment 6
Compound microalgae biological adsorption agent obtained in embodiment 3 carries out it to test except cadmium, the method is as follows: this is compound Microalgae biological adsorption agent is added containing in cadmium (Cd) waste water, and total cadmium (Cd) concentration is 2-20mg/L in suitable waste water, compound micro- The dosage of algae biological adsorption agent: 10-25g/L (waste water), 28-36 DEG C of adsorption temp, pH is controlled in 6-9.It is adsorbed by concussion The removal for completing cadmium (Cd) in waste water carries out quick magnetic separation to the microalgae biological adsorption agent in waste water after the completion of absorption, adopts With cadmium (Cd) concentration total in atomic absorption spectroscopy determination waste water, removal rate is calculated, and is imitated with the absorption of suspension chlorella Rate compares, and result is as shown in following table.
The adsorption efficiency of cadmium (Cd) under the different pH value of table 1
Cadmium in considerably higher waste water is achieved compared to suspension microalgae by the visible compound microalgae biological adsorption agent of data in table (Cd) removal rate, and by significantly improving stability of the chlorella in terms of heavy metals removal after compound fixation, in pH Good cadmium (Cd) Adsorption effect is achieved in the range of value 6-9.

Claims (10)

1. a kind of compound microalgae biological adsorption agent, which is characterized in that the preparation side of the compound microalgae biological adsorption agent Method is as follows:
(S.1) chlorella is cultivated: chlorella being cultivated in the medium, medium centrifugal separation obtains lower layer's concentration Microalgae biology;
(S.2) magnetic particle compounds: the microalgae biology dilution of concentration, and and magnetic Fe3O4Nanoparticle is compounded, and is completed micro- Frustule and magnetic Fe3O4Absorption between nanoparticle is fixed;
(S.3) prepared by immobilized microspheres: then middle addition sodium alginate in Xiang Shangshu solution is added drop-wise to CaCl2In solution, preparation Immobilized microspheres out, i.e., compound microalgae biological adsorption agent.
2. a kind of compound microalgae biological adsorption agent according to claim 1, which is characterized in that the step (S.1) Middle culture medium is BG11 culture medium, and the centrifugation rate is 3000-5000 rpm, and centrifugation time is 5-10 min.
3. a kind of compound microalgae biological adsorption agent according to claim 1, which is characterized in that the step (S.2) It is middle to be diluted using microalgae biology of the sterile water to concentration, adjust the OD of concentrate680For 1-1.5.
4. a kind of compound microalgae biological adsorption agent according to claim 1, which is characterized in that the step (S.2) Middle magnetic Fe3O4Nanoparticle the preparation method is as follows: using FeCl3、FeSO4Acidic iron salt solutions are prepared with hydrochloric acid, make Fe3+、 Fe2+Molar ratio with HCl is (1.0-2.5): 1:1, which is added drop-wise in the ammonium hydroxide that mass fraction is 20%-30%, molysite The volume ratio of solution and ammonium hydroxide is 1:3-1:5, is stirred evenly, and after coloured product becomes brown, staticly settles and carries out magnetic force point From, extra liquid is gone, the precipitating of bottom is sucked with magnet and distilled water is added and cleans 3-4 times, filtering acquisition Fe3O4, warp 36 ~ 72 h of vacuum freeze drying, is prepared into magnetic Fe3O4Nanoparticle.
5. a kind of compound microalgae biological adsorption agent described according to claim 1 or 3 or 4, which is characterized in that the step (S.2) magnetic Fe in3O4The additive amount of nanoparticle is to add magnetic Fe in every liter of algae solution3O40.2 ~ 0.4 g of nanoparticle.
6. a kind of compound microalgae biological adsorption agent described according to claim 1 or 3 or 4, which is characterized in that the step (S.2) compounding condition is isothermal vibration 2-4 days in.
7. a kind of compound microalgae biological adsorption agent according to claim 1, which is characterized in that the step (S.3) The mass fraction concentration of middle sodium alginate is 5%-7%, CaCl2The mass concentration of solution is 3.5%.
8. a kind of compound microalgae biological adsorption agent according to claim 1 or claim 7, which is characterized in that the step (S.3) in, the diameter of immobilized microspheres obtained is 2-5 mm, and the biomass containing microalgae is 1.0 × 10 in immobilized microspheres9 -6.0×109cell/g。
9. the method for cadmium, feature in a kind of microalgae biological adsorption agent absorption waste water compound as obtained in claim 1 ~ 8 It is, the method is as follows: the compound microalgae biological adsorption agent is added in cadmium wastewater, concussion absorption is completed in waste water The removal of cadmium carries out quick magnetic separation to the microalgae biological adsorption agent in waste water after the completion of absorption.
10. the method for cadmium in compound microalgae biological adsorption agent absorption waste water according to claim 9, which is characterized in that The concentration of cadmium is 2-20 mg/L in the cadmium wastewater, and the dosage of compound microalgae biological adsorption agent is 10-25 g/L, Adsorption temp is 28-36 DEG C, pH value 6-9.
CN201811353808.2A 2018-11-14 2018-11-14 A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water Pending CN109395700A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811353808.2A CN109395700A (en) 2018-11-14 2018-11-14 A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811353808.2A CN109395700A (en) 2018-11-14 2018-11-14 A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water

Publications (1)

Publication Number Publication Date
CN109395700A true CN109395700A (en) 2019-03-01

Family

ID=65473325

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811353808.2A Pending CN109395700A (en) 2018-11-14 2018-11-14 A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water

Country Status (1)

Country Link
CN (1) CN109395700A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110627218A (en) * 2019-09-18 2019-12-31 湖南南山矿泉水有限公司 Method for treating wastewater in mineral water production process
CN110627217A (en) * 2019-09-18 2019-12-31 湖南南山矿泉水有限公司 Pretreatment method for drinking water
CN110639476A (en) * 2019-08-20 2020-01-03 华南农业大学 Heavy metal adsorbent based on alkaline residue recycling and preparation method and application thereof
CN114231455A (en) * 2021-12-21 2022-03-25 南华大学 Biological pellet, immobilized microsphere, preparation method and application thereof
CN114733508A (en) * 2022-04-29 2022-07-12 华中科技大学 Microalgae biological Johnson catalyst and preparation method and application thereof
US11891312B1 (en) 2023-03-10 2024-02-06 King Saud University Magnetic hydrochar synthesized from microalgal biomass

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102614839A (en) * 2012-04-10 2012-08-01 湖南大学 Compound magnetic biological adsorbent and preparation method for same
CN102616912B (en) * 2012-04-10 2013-05-29 湖南大学 Method for adsorbing lead in wastewater by using composite magnetic biological adsorbent
CN107937382A (en) * 2017-12-26 2018-04-20 安徽仁维环保工程科技有限公司 A kind of preparation method of immobilized microalgae
CN107964544A (en) * 2018-01-22 2018-04-27 武汉净宇微藻科技有限公司 A kind of microalgae algae ball and process for fixation
CN108424906A (en) * 2018-04-04 2018-08-21 江南大学 A kind of method of Immobilized cells culture processing breeding wastewater

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102614839A (en) * 2012-04-10 2012-08-01 湖南大学 Compound magnetic biological adsorbent and preparation method for same
CN102616912B (en) * 2012-04-10 2013-05-29 湖南大学 Method for adsorbing lead in wastewater by using composite magnetic biological adsorbent
CN107937382A (en) * 2017-12-26 2018-04-20 安徽仁维环保工程科技有限公司 A kind of preparation method of immobilized microalgae
CN107964544A (en) * 2018-01-22 2018-04-27 武汉净宇微藻科技有限公司 A kind of microalgae algae ball and process for fixation
CN108424906A (en) * 2018-04-04 2018-08-21 江南大学 A kind of method of Immobilized cells culture processing breeding wastewater

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
ANTONIO CARLOS AUGUSTO DA COSTA,ET AL: "METALS BIOSORPTION BY SODIUM ALGINATE IMMOBILIZED CHLORELLA HOMOSPHAERA CELLS", 《BIOTECHNOLOGY》 *
CHRISTIAN VALDEZ, ET AL: "Analysis of removal of cadmium by action of immobilized chlorella sp. Micro-algae in alginate beads", 《F1000RESEARCH》 *
刘志媛,等: "《海藻生物技术》", 31 July 2015, 海洋出版社 *
廖鹏飞,等: "钝顶螺旋藻磁性生物吸附剂的制备及对铬(VI)的吸附性能", 《中南大学学报(自然科学版)》 *
陈小霞,等: "固定化小球藻去除Cr6+的研究", 《海洋通报》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110639476A (en) * 2019-08-20 2020-01-03 华南农业大学 Heavy metal adsorbent based on alkaline residue recycling and preparation method and application thereof
CN110639476B (en) * 2019-08-20 2020-12-11 华南农业大学 Heavy metal adsorbent based on alkaline residue recycling and preparation method and application thereof
CN110627218A (en) * 2019-09-18 2019-12-31 湖南南山矿泉水有限公司 Method for treating wastewater in mineral water production process
CN110627217A (en) * 2019-09-18 2019-12-31 湖南南山矿泉水有限公司 Pretreatment method for drinking water
CN114231455A (en) * 2021-12-21 2022-03-25 南华大学 Biological pellet, immobilized microsphere, preparation method and application thereof
CN114733508A (en) * 2022-04-29 2022-07-12 华中科技大学 Microalgae biological Johnson catalyst and preparation method and application thereof
US11891312B1 (en) 2023-03-10 2024-02-06 King Saud University Magnetic hydrochar synthesized from microalgal biomass

Similar Documents

Publication Publication Date Title
CN109395700A (en) A kind of method of cadmium in compound microalgae biological adsorption agent and its adsorbent absorption waste water
Kaplan Absorption and adsorption of heavy metals by microalgae
Santos et al. Selenium contaminated waters: An overview of analytical methods, treatment options and recent advances in sorption methods
CN112657465B (en) Preparation method of magnetic biochar and method for treating tailing wastewater
CN109225163A (en) A kind of method of cadmium in compound magnetic microalgae biological adsorption agent and its absorption waste water
Prasad et al. Biosorption of lead by Pleurotus florida and Trichoderma viride
CN111732156B (en) Method for inhibiting release of polycyclic aromatic hydrocarbons in rice and crab co-culture paddy field sediment polluted by medium and light polycyclic aromatic hydrocarbons
CN109174026A (en) A kind of method of chromium in compound microalgae biological adsorption agent microballoon and its absorption waste water
Murugesan et al. Biosorption of cadmium by live and immobilized cells of Spirulina platensis
CN102616912B (en) Method for adsorbing lead in wastewater by using composite magnetic biological adsorbent
CN102614839B (en) Compound magnetic biological adsorbent and preparation method for same
CN108587915B (en) Chlorella W5 capable of removing heavy metals in water with high heavy metal content and application thereof
Ali et al. Fungal remediation of Cd (ii) from wastewater using immobilization techniques
Gu et al. Enhanced Pb (II) removal by green alga Neochloris oleoabundans cultivated in high dissolved inorganic carbon cultures
CN110104833A (en) Water body nitrate cleanser and its application
CN107893064A (en) The preparation method and applications of the fixed microalgae bead of charcoal polyvinyl alcohol joint
Tam et al. Removal of copper by free and immobilized microalga, Chlorella vulgaris
CN109576160B (en) Chlorella W3 capable of removing heavy metals in water with high heavy metal content and application thereof
CN109133358A (en) A method of aquatic products processing wastewater is handled using chlorella and extracts diesel oil
Katircioğlu et al. Chromium (VI) biosorption from aqueous solutions by free and immobilized biomass of Oscillatoria sp. H1 isolated from freshwater
CN108993425A (en) A kind of compound biological adsorption agent and its application
CN106745592B (en) It is a kind of with heavy metal ion adsorbed and detection function composite flocculation agent and preparation method thereof
CN112774625A (en) Zirconium oxide doped magnetic high-surface active carbon composite material, preparation method and application
CN1915849A (en) Method for preparing composite assembled object of magnetic ferriferous oxide/ molecular sieve of Nano zeolite
CN112062281B (en) Method for repairing arsenic pollution of saline-alkali water body by using blue algae-biomembrane complex

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20190301