CN103253776B - Semi-coke microbial carrier and preparation method thereof - Google Patents

Semi-coke microbial carrier and preparation method thereof Download PDF

Info

Publication number
CN103253776B
CN103253776B CN201310202697.6A CN201310202697A CN103253776B CN 103253776 B CN103253776 B CN 103253776B CN 201310202697 A CN201310202697 A CN 201310202697A CN 103253776 B CN103253776 B CN 103253776B
Authority
CN
China
Prior art keywords
solution
blue charcoal
carrier
polyvinyl alcohol
semi
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.)
Active
Application number
CN201310202697.6A
Other languages
Chinese (zh)
Other versions
CN103253776A (en
Inventor
张垒
王丽娜
刘尚超
刘璞
付本全
段爱民
张楠
薛改凤
刘霞
王凯军
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.)
Wuhan Wisco Green City Technology Development Co ltd
Original Assignee
Wuhan Iron and Steel Group Corp
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 Wuhan Iron and Steel Group Corp filed Critical Wuhan Iron and Steel Group Corp
Priority to CN201310202697.6A priority Critical patent/CN103253776B/en
Publication of CN103253776A publication Critical patent/CN103253776A/en
Application granted granted Critical
Publication of CN103253776B publication Critical patent/CN103253776B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention discloses a semi-coke microbial carrier and a preparation method thereof. The carrier is prepared from semi-coke, polyvinyl alcohol and a cross-linking agent according to the weight part ratio of 100-500:30-100:0.1-0.8. The method comprises the following steps: weighing the semi-coke according to a weight part ratio, adding the semi-coke into a strong acid solution and a strong base solution, and treating and drying to obtain a semi-coke substrate; weighing the polyvinyl alcohol solution and cross-linking agent solution with relative weight according to the weight part ratio, and cross-linking; and adding the semi-coke substrate into the cross-linked polyvinyl alcohol solution, stirring for 2-5 hours, demolding, drying, cooling, pelleting or cutting and forming to obtain the carbon microbial film carrier. By utilizing the large specific surface area (more than 300m<2>/g) and excellent adsorption performance of the modified semi-coke, the adsorption capacity and film culturing amount of the carrier on the microbes and pollutants can be improved, the carrier is further suitable for treatment of high-concentration organic wastewater, and the carrier has high impact load resistance.

Description

Blue charcoal microbe carrier and preparation method thereof
Technical field
The invention belongs to field of waste water treatment, be specifically related to a kind of blue charcoal microbe carrier and preparation method thereof.
Technical background
Since the successful operation of biological filter, biomembrance process because of degradation capability strong, duration of contact is short, and the little and cost of investment of floor space is low etc., and advantage is able to fast-developing application in recent years.Ripe because of Wastewater Treated by Activated Sludge Process waster water process, the advantage such as operation, maintenance cost are low remains domestic water and processes the most frequently used method.But activated sludge process floor space is large, excess sludge is many, denitrification effect is poor, the shortcomings such as sludge bulking and sludge loss easily occur, people are by adopting biomembrance process to improve the performance of biochemical treatment.And as microbial carrier material, determined water treatment effect and mass-transfer efficiency in reactor in biomembrance process.Therefore, bio-carrier is the core of biomembrance process water technology.Absorption between biology and bio-carrier, not only relevant with biological characteristic in conjunction with tightness degree, is also closely connected with bio-carrier material property.Therefore, the surface property of bio-carrier, voidage, specific surface area and material have material impact to the mass transfer of biological absorption, carrier and water treatment capacity.Can be used for the material of bio-carrier from inorganic materials (as pottery, rubble, slag, zeolite, gac etc.) to organic polymer material (industrial plastic, as polyethylene, polypropylene, polyvinyl chloride, polyphenyl alkene and various resins etc.) and synthetic organic-inorganic macromolecular material etc., not only consider the performance (physical strength, stability, Biostatic, close hydrophobic nature etc.), specific surface area of carrier, biological consistency etc., also considered the factors such as the drawing materials of material, cost value, manufacturing conditions.
Domestic market widely used inorganic and organic microbial carrier/filler, there are many shortcomings in these bio-carriers, such as material cost is high, complete processing is complicated, also there is the environmental problems such as secondary pollution in part.The shortcomings such as such as the inorganic ceramic material adopting, ubiquity density is large, and porosity is low and specific surface area is little, and the interior fluidization power consumption of reactor is large; Most polymer organic carrier just comes from petrochemical industry derived product, as poor in its wetting abilities such as polypropylene, polyethylene, and microorganism colonization, microbial biomass etc. are poor, and the photodissociation in environment of part material, even environmental organism are had to certain toxicity.
Summary of the invention
The object of the invention is to overcome above-mentioned weak point, a kind of blue charcoal microbe carrier and preparation method thereof is provided.Not only biofilm is fast, microorganism capacity is large for this carrier, also for microorganism provides suitable nutrition source, and environmental sound, and the resource utilization method of a kind of economic, practical, the high added value simultaneously also providing for the blue charcoal of low value.
For achieving the above object, a kind of blue charcoal microbe carrier that the present invention is designed, this carrier is: Lan Tan ︰ Ju Yi Xi Chun ︰ linking agent=100 ~ 500 ︰ 30 ~ 100 ︰ 0.1 ~ 0.8 according to weight part ratio.
Further, this carrier is: Lan Tan ︰ Ju Yi Xi Chun ︰ linking agent=200 ~ 400 ︰ 40 ~ 80 ︰ 0.3 ~ 0.8 according to weight part ratio.
Again further, this carrier is: Lan Tan ︰ Ju Yi Xi Chun ︰ linking agent=240 ︰ 80 ︰ 0.6 according to weight part ratio.
Again further, described blue charcoal size is 15 ~ 300 orders.
Again further, described linking agent is glutaraldehyde, formaldehyde or oxalic dialdehyde.
The present invention also provides a kind of preparation method of blue charcoal microbe carrier, comprises the following steps:
1) by described weight part ratio, take blue charcoal, blue charcoal is added in strong acid solution, treatment time 2 ~ 5h;
2) the blue charcoal after processing is adopted to strong base solution dipping 0.5 ~ 2h, be washed till neutrality, then clean 1 ~ 3 time with tap water, dry 1 ~ 2h makes blue charcoal matrix;
3) by described weight part ratio, measure polyvinyl alcohol solution and the cross-linking agent solution of relative weight;
4) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 10 ~ 24h;
5) by step 2) the blue charcoal matrix of gained adds in the polyvinyl alcohol solution after crosslinked and stirs 2 ~ 5h, and polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
6) the blue charcoal matrix/polyvinyl alcohol blend of step 5) gained matter is poured on bright and clean glass plate or in the mould of the easily demoulding, dries or air-dry;
7) after demoulding, after taking-up, under 80 ~ 150 ℃ of conditions, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
As preferred version, in described step 1), blue charcoal size is 15 ~ 300 orders.
As preferred version, in described step 1), the mass concentration of strong acid solution is that 10 ~ 50% temperature are 80 ~ 100 ℃, and strong acid solution is salpeter solution, hydrochloric acid soln or sulphuric acid soln.
As preferred version, described step 2) in, the mass concentration of strong base solution is 6.4 ~ 31.7%, and drying temperature is 90 ~ 110 ℃, and strong base solution is sodium hydroxide solution, potassium hydroxide solution or aqua calcis.
As preferred version, in described step 3), polyvinyl alcohol solution quality solubility is 3 ~ 10%, and cross-linking agent solution is that mass concentration is 0.5 ~ 1.5% glutaraldehyde solution, formaldehyde solution or glyoxal solution.
Advantage of the present invention is as follows:
(1) utilize the huge specific surface area (>300m of the blue charcoal of modification 2/ g) and good absorption property, can improve carrier to the adsorptive power of microorganism and pollutent and biofilm amount, and then be conducive to adapt to the processing of high concentrated organic wastewater, and there is higher anti impulsion load ability;
(2) by controlling the burnt grain of blue charcoal and polyvinyl alcohol solution concentration, can regulate the density of this microbe carrier;
(3) this carrier polyvinyl alcohol is Biodegradable material, in the not enough situation of carbon source, can be used as microbe carbon source;
(4) this microbe carrier is drawn materials conveniently, good to bioaffinity, can be to environment, and the discarded carrier in system operational process enters biochemical sludge, can deliver to coal yard coal blending workshop and use as raw material or raw materials for sintering.
(5) to choose the particle diameter of blue charcoal be 15 ~ 300 orders in the present invention, conversion particle diameter diameter 1mm~0.05mm.Experiment shows, if particle diameter is too large, and while being greater than 300mu, biofilm carrier easily runs off together with mud; Particle diameter is less than 15 orders, and specific surface area is relatively little, and adsorptive power is poor, in addition, because blue charcoal, density own are large, easily sinks, and therefore, needs larger aeration just can be suspended in solution, also increases blower power, has caused energy consumption increase.Through experimental analysis, it is most suitable that particle diameter is selected 15~300 orders.
(6) preparation method of the present invention is simple, and required equipment is few, and preparation cost is low.
(7) the blue charcoal that the present invention selects claims again semicoke, fixed carbon is high, higher than resistance, chemically reactive is high, contain the characteristic that ash is low, sulfur is low and phosphorus is low, it is main mainly with low-temperature pyrolysis that blue charcoal is produced, pyrolysis temperature is generally 600 ℃ of left and right, high because having fixed carbon, volatile components content is high, very easily pore-forming, therefore specific surface area is larger, adsorptive power is stronger.The present invention utilizes blue charcoal particle porosity high, and characterization of adsorption is strong, and biological attachment amount is large, and after PVA blend masking, is convenient to germs collect in active sludge, sticks.
Accompanying drawing explanation
Fig. 1 is the blue charcoal microbe carrier scanning electron microscope (SEM) photograph (SEM) of the present invention.
Embodiment
Below in conjunction with specific embodiment, a kind of blue charcoal microbe carrier of the present invention and preparation method thereof is described in further detail.
Embodiment 1
1) taking 50g size is the blue charcoals of 200 objects, blue charcoal is added in the salpeter solution that 80 ℃ of mass concentrations are 10% to treatment time 4h;
2) the blue charcoal after processing is adopted under the sodium hydroxide solution normal temperature that mass concentration is 31.7% and floods 1h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 2h makes blue charcoal matrix;
3) 3g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 97mL100 ℃, obtains 3% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 3.2mL is 2.5%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 20h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 3h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 110 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.48g/cm 3, in solution, density is about 1.25g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 62h, record its chemical oxygen demand (COD) (COD) and surpass 90%, than adding bio-carrier, approximately do not improved 38%; Its total nitrogen (TN) clearance surpasses 45%, than adding bio-carrier, has not approximately improved 22%.
Embodiment 2
1) taking 10g size is the blue charcoals of 300 objects, blue charcoal is added in the salpeter solution that 100 ℃ of mass concentrations are 50% to treatment time 2h;
2) the blue charcoal after processing is adopted under the sodium hydroxide solution normal temperature that mass concentration is 20% and floods 0.5h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 80 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 6g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 94mL100 ℃, obtains 6% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 2mL is 0.5%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 10h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 2h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 150 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.42g/cm 3, in solution, density is about 1.15g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 55h, record its chemical oxygen demand (COD) (COD) and surpass 92%, than adding bio-carrier, approximately do not improved 35%; Its total nitrogen (TN) clearance surpasses 46%, than adding bio-carrier, has not approximately improved 21%.
Embodiment 3
1) taking 20g size is the blue charcoals of 15 objects, blue charcoal is added in the salpeter solution that 100 ℃ of mass concentrations are 20% to treatment time 5h;
2) the blue charcoal after processing is adopted under the aqua calcis normal temperature that mass concentration is 6.4% and floods 2h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 90 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 8g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 92mL100 ℃, obtains 8% polyvinyl alcohol solution;
4) measure the glutaraldehyde solution that the mass concentration of 2mL is 1.5%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 24h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 80 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.45g/cm 3, in solution, density is about 1.20g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 60h, record its chemical oxygen demand (COD) (COD) and surpass 90%, than adding bio-carrier, approximately do not improved 35%; Its total nitrogen (TN) clearance surpasses 45%, than adding bio-carrier, has not approximately improved 21%.
Embodiment 4
1) taking 40g size is the blue charcoals of 200 objects, blue charcoal is added in the hydrochloric acid soln that 100 ℃ of mass concentrations are 20% to treatment time 5h;
2) the blue charcoal after processing is adopted under the potassium hydroxide solution normal temperature that mass concentration is 10.4% and floods 0.5h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 4g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 96mL100 ℃, obtains 4% polyvinyl alcohol solution;
4) measure the formaldehyde solution that the mass concentration of 2mL is 1.5%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 24h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 110 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.42g/cm 3, in solution, density is about 1.10g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 50h, record its chemical oxygen demand (COD) (COD) and surpass 85%, than adding bio-carrier, approximately do not improved 30%; Its total nitrogen (TN) clearance surpasses 40%, than adding bio-carrier, has not approximately improved 15%.
Embodiment 5
1) taking 24g size is the blue charcoals of 200 objects, blue charcoal is added in the hydrochloric acid soln that 100 ℃ of mass concentrations are 20% to treatment time 5h;
2) the blue charcoal after processing is adopted under the potassium hydroxide solution normal temperature that mass concentration is 30% and floods 0.5h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 8g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 92mL100 ℃, obtains 8% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 4mL is 2.0%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 4h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 110 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.50g/cm 3, in solution, density is about 1.40g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 70h, record its chemical oxygen demand (COD) (COD) and surpass 95%, than adding bio-carrier, approximately do not improved 45%; Its total nitrogen (TN) clearance surpasses 55%, than adding bio-carrier, has not approximately improved 30%.
Embodiment 6
1) taking 50g size is the blue charcoals of 15 objects, blue charcoal is added in the hydrochloric acid soln that 80 ℃ of mass concentrations are 50% to treatment time 2h;
2) the blue charcoal after processing is adopted under the potassium hydroxide solution normal temperature that mass concentration is 31.7% and floods 2h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 3g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 97mL100 ℃, obtains 3% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 2.5mL is 1.0%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 24h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 150 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.80g/cm 3, in solution, density is about 1.45g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 60h, record its chemical oxygen demand (COD) (COD) clearance and surpass 95%, than adding bio-carrier, approximately do not improved 45%; Its total nitrogen (TN) clearance surpasses 60%, than adding bio-carrier, has not approximately improved 22%.
Embodiment 7
1) taking 25g size is the blue charcoals of 150 objects, blue charcoal is added in the salpeter solution that 90 ℃ of mass concentrations are 20% to treatment time 2h;
2) the blue charcoal after processing is adopted under the sodium hydroxide solution normal temperature that mass concentration is 15.9% and floods 1h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 5g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 95mL100 ℃, obtains 5% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 2.5mL is 1.0%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 24h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 150 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.70g/cm 3, in solution, density is about 1.32g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 60h, record its chemical oxygen demand (COD) (COD) clearance and surpass 92%, than adding bio-carrier, approximately do not improved 38%; Its total nitrogen (TN) clearance surpasses 55%, than adding bio-carrier, has not approximately improved 19%.
Embodiment 8
1) taking 10g size is the blue charcoals of 300 objects, blue charcoal is added in the salpeter solution that 100 ℃ of mass concentrations are 10% to treatment time 5h;
2) the blue charcoal after processing is adopted under the sodium hydroxide solution normal temperature that mass concentration is 6.4% and floods 0.5h, be washed till neutrality, then clean 1 ~ 3 time with tap water, under 100 ℃ of conditions, dry 1h makes blue charcoal matrix;
3) 10g polyvinyl alcohol (polymerization degree is greater than 1750) is dissolved in to return stirring 8h in the boiling water of 90mL100 ℃, obtains 10% polyvinyl alcohol solution;
4) measure the glyoxal solution that the mass concentration of 2mL is 0.5%;
5) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 24h;
6) by step 2) in blue charcoal matrix add in the polyvinyl alcohol solution after crosslinked and stir 5h, polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
7) blue charcoal matrix/polyvinyl alcohol blend matter in step 6) is poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
8) after demoulding, after taking-up, in the baking box of 80 ℃, carry out bake drying, cooling after, granulation or excision forming, obtain carbonaceous microbial membrane carrier.
After testing, the prepared dry rear density of the blue charcoal bio-carrier of finished product of the present embodiment method is 0.45g/cm 3, in solution, density is about 1.20g/cm 3, under the disturbance of aeration solution, can be suspended in solution.In utilizing the experiment of aerobic, anaerobism all-in-one fluidization bed biofilm reactor Treatment of Wastewater in Coking, at hydraulic detention time (HRT) 60h, record its chemical oxygen demand (COD) (COD) and surpass 90%, than adding bio-carrier, approximately do not improved 35%; Its total nitrogen (TN) clearance surpasses 45%, than adding bio-carrier, has not approximately improved 21%.

Claims (4)

1. a preparation method for blue charcoal microbe carrier, this carrier according to weight part ratio is: blue charcoal ︰ gathers second alkene alcohol ︰ linking agent=200~400 ︰ 40~80 ︰ 0.3~0.8, and wherein, described linking agent is glutaraldehyde, formaldehyde or oxalic dialdehyde; It is characterized in that: comprise the following steps:
1) by described weight part ratio, take blue charcoal, blue charcoal is added in strong acid solution, treatment time 2~5h;
2) the blue charcoal after processing is adopted to strong base solution dipping 0.5~2h, be washed till neutrality, then clean 1~3 time with tap water, dry 1~2h makes blue charcoal matrix;
3) by described weight part ratio, measure glyoxal solution or formaldehyde solution or the glutaraldehyde solution that polyvinyl alcohol solution that the mass concentration of relative weight is 3~10% and mass concentration are 0.5~1.5%;
4) polyvinyl alcohol solution and cross-linking agent solution are cross-linked to 10~24h;
5) by step 2) the blue charcoal matrix of gained adds in the polyvinyl alcohol solution after crosslinked and stirs 2~5h, and polyvinyl alcohol gel can be evenly coated in above blue charcoal matrix;
6) by step 5) blue charcoal matrix/polyvinyl alcohol blend matter be poured on bright and clean glass plate or the mould of the easily demoulding in, dry or air-dry;
7) after demoulding, after taking-up, under 80~150 ℃ of conditions, carry out bake drying, cooling after, granulation or excision forming, obtain blue carbonaceous microbial membrane carrier.
2. the preparation method of blue charcoal microbe carrier according to claim 1, is characterized in that: described step 1), blue charcoal size is 15~300 orders.
3. according to the preparation method of blue charcoal microbe carrier described in claim 1 or 2, it is characterized in that: described step 1), the mass concentration of strong acid solution is that 10~50% temperature are 80~100 ℃, and strong acid solution is salpeter solution, hydrochloric acid soln or sulphuric acid soln.
4. the product that described in a claim 1, the preparation method of blue charcoal microbe carrier obtains.
CN201310202697.6A 2013-05-28 2013-05-28 Semi-coke microbial carrier and preparation method thereof Active CN103253776B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310202697.6A CN103253776B (en) 2013-05-28 2013-05-28 Semi-coke microbial carrier and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310202697.6A CN103253776B (en) 2013-05-28 2013-05-28 Semi-coke microbial carrier and preparation method thereof

Publications (2)

Publication Number Publication Date
CN103253776A CN103253776A (en) 2013-08-21
CN103253776B true CN103253776B (en) 2014-11-12

Family

ID=48958055

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310202697.6A Active CN103253776B (en) 2013-05-28 2013-05-28 Semi-coke microbial carrier and preparation method thereof

Country Status (1)

Country Link
CN (1) CN103253776B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104609567B (en) * 2013-11-05 2017-01-18 中国石油化工股份有限公司 Preparation method of suspended packing bioreactor and application thereof
CN104628123B (en) * 2015-01-28 2016-06-01 苏州赛华仪控股份有限公司 A kind of modification biological slag microbe carrier and its preparation method
CN107285851A (en) * 2017-06-15 2017-10-24 西施生态科技股份有限公司 A kind of matrix of ornamental plant introducing and planting and its preparation
CN108217976A (en) * 2018-01-29 2018-06-29 青岛净界生态技术有限公司 A kind of bionic aquatic weed method of modifying
CN110980932B (en) * 2019-11-26 2022-06-03 兰州交通大学 Oil shale semicoke/polyvinyl alcohol composite immobilized carrier and preparation method thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1868919A (en) * 2006-05-29 2006-11-29 南昌大学 Suspension microorganism carrier and its preparation method
CN101428901A (en) * 2008-12-09 2009-05-13 沈阳师范大学 Bamboo charcoal-polyvinyl formal biological carrier and preparation thereof
CN102120178A (en) * 2011-02-11 2011-07-13 广东工业大学 Active semicoke adsorbing agent and preparation method thereof
CN102250867A (en) * 2011-06-17 2011-11-23 清华大学 Poly(vinyl alcohol)-immobilized microorganism particles and preparation method thereof
CN102874805A (en) * 2012-09-17 2013-01-16 浙江海亮环境材料有限公司 Method for preparing porous carbon for wastewater treatment

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
MXPA00001414A (en) * 1999-11-23 2002-03-08 Westvaco Corp Coated activated carbon.

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1868919A (en) * 2006-05-29 2006-11-29 南昌大学 Suspension microorganism carrier and its preparation method
CN101428901A (en) * 2008-12-09 2009-05-13 沈阳师范大学 Bamboo charcoal-polyvinyl formal biological carrier and preparation thereof
CN102120178A (en) * 2011-02-11 2011-07-13 广东工业大学 Active semicoke adsorbing agent and preparation method thereof
CN102250867A (en) * 2011-06-17 2011-11-23 清华大学 Poly(vinyl alcohol)-immobilized microorganism particles and preparation method thereof
CN102874805A (en) * 2012-09-17 2013-01-16 浙江海亮环境材料有限公司 Method for preparing porous carbon for wastewater treatment

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
改性兰炭对焦化废水生化出水的吸附特性;王丽娜等;《工业水处理》;20120930;第32卷(第9期);第49-51页 *
王丽娜等.改性兰炭对焦化废水生化出水的吸附特性.《工业水处理》.2012,第32卷(第9期), *

Also Published As

Publication number Publication date
CN103253776A (en) 2013-08-21

Similar Documents

Publication Publication Date Title
CN103253776B (en) Semi-coke microbial carrier and preparation method thereof
CN103159330B (en) Porous light-weight carbon-based biological carrier and preparation method thereof
CN110918061B (en) Biomass waste activated carbon, preparation method thereof and application of biomass waste activated carbon in treatment of nitrophenol compounds in wastewater
CN101445388A (en) Porous ceramic grain for disposing wastewater and method for preparing same
CN102351306B (en) Mangneto modified ceramsite filler, preparation method thereof and application of modified filler in wastewater processing
CN111892175B (en) Preparation method and application of porous carbon reinforced microorganism biofilm carrier material
CN115043479B (en) Nitrogen-doped biochar as well as preparation method and application thereof
Gan et al. Activation of waste MDF sawdust charcoal and its reactive dye adsorption characteristics
CN111204817B (en) Magnetic composite carbon prepared from harmful algal bloom and plastic and preparation method thereof
CN103342412B (en) Coke particle biomembrane carrier and preparation method thereof
CN110523379A (en) A kind of low cost preparation method of porous charcoal
CN104261570A (en) Livestock and poultry breeding anaerobic wastewater purifying agent
CN102765866A (en) Method for recycling urban sludge
CN102757047A (en) Method for preparing cylindrical sludge-based activated carbon
CN100482599C (en) Biological sponge iron preparation and its uses in water disposal
CN109772472B (en) Method for preparing carbon catalytic material from high-water-content excess sludge
CN112624328B (en) Positive-charge solid slow-release carbon source and preparation method and application thereof
CN105195095A (en) Method for utilizing sludge fermented waste for preparing heavy metal ions absorbent
CN115108705B (en) Preparation method, product and application of modified magnetic sludge peat
WO2009081555A1 (en) Method for treatment of organic liquid waste, and recycled fuel carbon
CN115920840A (en) Sludge-based activated carbon adsorbent and preparation method and application thereof
Chen et al. Adsorption behavior of activated carbon derived from pyrolusite-modified sewage sludge: equilibrium modeling, kinetic and thermodynamic studies
CN113171751A (en) Preparation method and application of pyrophosphate modified biochar
CN110734127A (en) carbon composite nano zero-valent metal porous functional material, preparation method and application thereof
CN114505051B (en) Adsorbent for treating low COD sewage and preparation method and application thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20170718

Address after: 430083, Hubei Wuhan Qingshan District Factory No. 2 Gate joint stock company organs

Patentee after: Wuhan iron and Steel Company Limited

Address before: 430080 Wuchang, Hubei Friendship Road, No. A, block, floor 999, 15

Patentee before: Wuhan Iron & Steel (Group) Corp.

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20190327

Address after: 430080 122, metallurgical Avenue, Qingshan District, Wuhan, Hubei

Patentee after: Wuhan green city construction and Development Co., Ltd.

Address before: 430083 Organs of Changqian No. 2 Gate Co., Ltd., Qingshan District, Wuhan City, Hubei Province

Patentee before: Wuhan iron and Steel Company Limited

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20200715

Address after: Gate 1, changqian, Qingshan District, Wuhan City, Hubei Province

Patentee after: Wuhan WISCO Green City Technology Development Co.,Ltd.

Address before: 430080 Wuhan, Heilongjiang Province, Qingshan District, metallurgical Road, No. 122, No.

Patentee before: BAOWU GREEN CITY CONSTRUCTION Co.,Ltd.