CN116969592A - Composite carbon source and preparation method and application thereof - Google Patents

Composite carbon source and preparation method and application thereof Download PDF

Info

Publication number
CN116969592A
CN116969592A CN202311227892.4A CN202311227892A CN116969592A CN 116969592 A CN116969592 A CN 116969592A CN 202311227892 A CN202311227892 A CN 202311227892A CN 116969592 A CN116969592 A CN 116969592A
Authority
CN
China
Prior art keywords
glycerol
carbon source
composite carbon
acid
solution
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
CN202311227892.4A
Other languages
Chinese (zh)
Other versions
CN116969592B (en
Inventor
杨文凯
包国强
郝文奇
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.)
Jiangsu United Water Technology Co ltd
Shanghai Boruisi Environmental Technology Co ltd
Original Assignee
Shanghai Boruisi Environmental Technology Co ltd
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 Shanghai Boruisi Environmental Technology Co ltd filed Critical Shanghai Boruisi Environmental Technology Co ltd
Priority to CN202311227892.4A priority Critical patent/CN116969592B/en
Publication of CN116969592A publication Critical patent/CN116969592A/en
Application granted granted Critical
Publication of CN116969592B publication Critical patent/CN116969592B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • C02F3/28Anaerobic digestion processes
    • 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
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/06Nutrients for stimulating the growth of microorganisms

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

The invention relates to the technical field of carbon sources for denitrification of sewage, in particular to a composite carbon source and a preparation method and application thereof. A preparation method of a composite carbon source comprises the following steps: 1) Adding acid into the crude glycerol, and performing acidification treatment to obtain first glycerol liquid of first acidified oil; 2) Adding an alkaline solution into the first glycerol solution, regulating the pH value, standing for layering, and removing the precipitate to obtain a second glycerol solution; 3) Distilling the first acidified oil under reduced pressure, and heating to obtain third glycerin solution and first residues; 4) Adding water into the first residue, centrifuging, evaporating and condensing to obtain fourth glycerol liquid and second residue; 5) And mixing the second glycerol solution and the fourth glycerol solution, and adding saccharides, alcohols, acids and denitrification accelerators to obtain the composite carbon source. Compared with a single carbon source, the crude glycerol composite carbon source has higher utilization rate and selectivity. By complexing with other carbon sources, microbial growth and metabolism can be promoted.

Description

Composite carbon source and preparation method and application thereof
Technical Field
The invention relates to the technical field of carbon sources for denitrification of sewage, in particular to a composite carbon source and a preparation method and application thereof.
Background
Along with the development of economy and society, the eutrophication of the water body is increasingly serious, and the nitrogen and phosphorus content in the water body is increased. High-efficiency stable denitrification and dephosphorization are key links of the current sewage treatment, and denitrification biological denitrification by utilizing the metabolism of microorganisms is most economical and effective.
Traditionally, sewage is biologically denitrified to remove nitrogen from carbon sources such as glucose, sodium acetate, starch, and the like. However, these carbon sources are costly and burden the environment. Accordingly, more and more research has been devoted in recent years to developing alternative carbon sources at low cost.
Disclosure of Invention
In view of the above-described drawbacks of the prior art, a first aspect of the present invention provides a method for preparing a composite carbon source, comprising the steps of:
1) Mixing crude glycerol with acid, and performing acidification treatment to obtain first acidified oil and first glycerol; under alkaline conditions, glycerin, soap, methanol and methyl ester are mixed together into a gel, and it is very difficult to separate them one by sedimentation or centrifugation. Therefore, in the separation of glycerin, the lower layer liquid needs to be neutralized to an appropriate pH with an acid. In this way, they can be separated by sedimentation or centrifugation.
2) Regulating the pH value of the first glycerol solution obtained in the step 1) to be 8.0-8.5, standing for layering, and removing the precipitate to obtain second glycerol solution; after the pH adjustment, the pH needs to be adjusted to be neutral in order to have better practicality in use.
3) Distilling the first acidified oil obtained in the step 1) under reduced pressure, and heating to obtain third glycerin solution and first residues;
4) Adding water into the first residue obtained in the step 3), centrifuging, evaporating and condensing to obtain fourth glycerol liquid and second residue;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding saccharides, alcohols, acids and denitrification promoters to obtain the composite carbon source;
in step 1), the crude glycerol is derived from biodiesel by-products.
Preferably, at least one of the following technical features is included:
11 In step 1), the acid is selected from one or more of formic acid, acetic acid, hydrochloric acid and sulfuric acid;
12 In step 1), an acid is added to a pH of 4.0 to 4.5, for example, 4.0 to 4.1,4.1 to 4.2,4.2 to 4.3,4.3 to 4.4, 4.4 to 4.5, etc.
13 In step 1), the acidification treatment time is 30-40min, for example, 30-31min,30-32min,30-33min,30-34min,30-35min,30-36min,30-37min,30-38min,30-39min,30-40min, etc.
14 Step 1) further comprising transferring the first glycerol solution to a neutralization reactor.
Preferably comprises
21 In the step 2), the reagent for adjusting the pH is an alkaline solution;
22 In the step 2), the second glycerol solution is subjected to impurity removal treatment.
Preferably, at least one of the following technical features is included:
211 In feature 21), the alkaline solution is selected from barium hydroxide;
221 In feature 22), the method of removing impurities is: allowing the second glycerol solution to sequentially pass through a cation exchange column, an anion exchange column and an anion and cation exchange column.
Preferably, at least one of the following technical features is included:
31 In step 3), the vacuum degree of the reduced pressure distillation is controlled to be 0.15 to 0.17kPa, for example, 0.15 to 0.16kPa,0.16 to 0.17kPa;
32 Step 3), heating to 164-204 ℃;
33 In the step 3), the third glycerol liquid is refined glycerol.
Preferably, at least one of the following technical features is included:
41 In step 4), the volume ratio of the first residue to the water is 1: (0.75-1.15), for example, may be 1:0.75,1:0.85,1:1,1:1.05, etc.
42 In step 4), the centrifugal separation device is a double-pushing centrifugal machine, preferably, the centrifugal separation rotating speed is 450-550r/min, for example, 450-460r/min,450-470r/min,450-480r/min,450-490r/min,450-500r/min,450-510r/min,450-520r/min,450-530r/min,450-540r/min, 460-550r/min and the like.
43 In the step 4), the evaporation and condensation device is a thin film evaporator;
44 In step 4), the second residue is asphaltenes.
Preferably, at least one of the following technical features is included:
51 In step 5), the saccharide is selected from one or more of glucose, galactose and fructose;
52 In step 5), the alcohol is selected from one or more of methanol, ethanol, glycol, glycerol and butanol;
53 Step 5), the acid is selected from one or more of acetic acid, propionic acid, n-butyric acid and isobutyric acid;
the added sugar substances are monosaccharide carbon sources, and the monosaccharide compound is an environment-friendly and efficient additional carbon source, and can be utilized by microorganisms without long-time hydrolysis process; the added acid substances are volatile fatty acids, are small molecular organic acids, are easily utilized by denitrifying bacteria, and have good denitrification effect; the added alcohol compound has the characteristics of low cost and good denitrification effect as an additional carbon source.
54 In step 5), the total mass of the second glycerol liquid and the fourth glycerol liquid is as follows: quality of saccharides: alcohol mass: acid mass= (60-70): (5-10): (5-10): (5-10);
55 In the step 5), the denitrification promoter is sulfur and metal biological modified carbon, the metal biological modified carbon is selected from any one of iron, magnesium, manganese and nickel, and the preparation method of the metal biological modified carbon comprises the following steps: and adding the bamboo blocks or the wood blocks into a metal salt solution for soaking treatment, drying, and sequentially performing carbonization treatment and crushing treatment to obtain the metal modified biochar.
The metal element in the metal modified biochar contained in the denitrification promoter plays a role in regulating the surface charge of a carbon source, can promote the adsorption and removal of nitrate, and sulfur in the contained sulfur can provide an electron donor for the process of reducing nitrate by denitrifying bacteria, so that the metal element is matched with the heterotrophic denitrification process to jointly promote the removal of nitrate, and the biological denitrification efficiency can be further improved.
Preferably, at least one of the following technical features is included:
551 In feature 55), the mass ratio of the sulfur to the composite carbon source is (0.5-1): 100, for example, may be 0.5: 100. 0.6: 100. 0.7: 100. 0.8: 100. 0.9:100, etc.
552 In feature 55), the mass ratio of the metal bio-modified carbon to the composite carbon source is (0.05-0.1): 100, for example, may be 0.05: 100. 0.06: 100. 0.07: 100. 0.08: 100. 0.09:100, etc.
The second aspect of the invention provides a composite carbon source, which is prepared by the preparation method of the composite carbon source.
A third aspect of the present invention provides the use of the above-described composite carbon source for denitrification of wastewater.
As described above, the preparation method of the composite carbon source provided by the invention has the following beneficial effects:
1) The invention provides a method and a composition for fermenting, purifying and then compounding a composite carbon source by taking crude glycerol as a main raw material. The method comprises the steps of purifying the biodiesel byproduct crude glycerol and compounding with other carbon sources, so that the waste utilization of the crude glycerol is solved, and simultaneously, the utilization rate and the selectivity of microorganisms on the carbon sources are increased by utilizing organic matters in the biodiesel.
2) The crude glycerol in the invention is a low-cost and easily-obtained carbon source, can obviously reduce the production cost of denitrification carbon sources, and has good economic benefit when applied on a large scale. Compared with a single carbon source, the crude glycerol composite carbon source has higher utilization rate and selectivity. Through compounding with other carbon sources, the microbial growth and metabolism can be promoted, and the sewage denitrification is facilitated.
3) The invention uses the crude glycerine as the main raw material to produce the composite carbon source, has stronger economy, and solves the problem of disposal of the crude glycerine.
4) The preparation method of the composite carbon source provided by the invention is simple and feasible, and is easy for large-scale production and application.
Detailed Description
Other advantages and effects of the present invention will become apparent to those skilled in the art from the following disclosure, which describes the embodiments of the present invention with reference to specific examples. The invention may be practiced or carried out in other embodiments that depart from the specific details, and the details of the present description may be modified or varied from the spirit and scope of the present invention. It should be understood that the process equipment or devices not specifically identified in the examples below are all conventional in the art.
Furthermore, it is to be understood that the reference to one or more method steps in this disclosure does not exclude the presence of other method steps before or after the combination step or the insertion of other method steps between these explicitly mentioned steps, unless otherwise indicated; it should also be understood that the combined connection between one or more devices/means mentioned in the present invention does not exclude that other devices/means may also be present before and after the combined device/means or that other devices/means may also be interposed between these two explicitly mentioned devices/means, unless otherwise indicated. Moreover, unless otherwise indicated, the numbering of the method steps is merely a convenient tool for identifying the method steps and is not intended to limit the order of arrangement of the method steps or to limit the scope of the invention in which the invention may be practiced, as such changes or modifications in their relative relationships may be regarded as within the scope of the invention without substantial modification to the technical matter.
Example 1
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH value is about 4.0, acidizing for 30min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding glucose, ethylene glycol and acetic acid, wherein the mass fraction of the glucose is 10%, the mass fraction of the ethylene glycol is 5%, and the mass fraction of the acetic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.75, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect. Wherein BOD5 is an important index for indirectly representing the pollution degree of the water body by organic matters by using the dissolved oxygen amount consumed by the metabolism of microorganisms.
Example 2
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH value is about 4.0, acidizing for 35min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding glucose, ethylene glycol and acetic acid, wherein the mass fraction of the glucose is 10%, the mass fraction of the ethylene glycol is 5%, and the mass fraction of the acetic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.78, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect.
Example 3
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH value is about 4.0, acidizing for 40min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding glucose, ethylene glycol and methyl acetic acid, wherein the mass fraction of the glucose is 10%, the mass fraction of the ethylene glycol is 5%, and the mass fraction of the acetic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.80, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect.
Example 4
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH value is about 4.0, acidizing for 30min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding fructose, glycerol and propionic acid, wherein the mass fraction of the fructose is 10%, the mass fraction of the glycerol is 5%, and the mass fraction of the propionic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.76, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect.
Example 5
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH is about 4.2, acidizing for 30min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding fructose, glycerol and propionic acid, wherein the mass fraction of the fructose is 10%, the mass fraction of the glycerol is 5%, and the mass fraction of the propionic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.78, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect.
Example 6
1) Adding 0.32ml of analytically pure acetic acid into 1000g of crude glycerol to ensure that the pH value is about 4.5, acidizing for 30min to obtain upper first acidized oil and lower first glycerol liquid, and transferring the first glycerol liquid into a neutralization reactor;
2) Adding barium hydroxide into the first glycerol solution obtained in the step 1), regulating the pH to 8.0, standing for layering to obtain second glycerol solution, and removing various impurities from a cation exchange column, an anion exchange column and an anion exchange column generated by the generated second glycerol solution to generate precipitate and discharge the precipitate from the bottom of the neutralization reactor;
3) Performing reduced pressure distillation on the first acidified oil obtained in the step 1), controlling the vacuum degree of reduced pressure distillation at 0.15kPa, heating to 204 ℃ to obtain third glycerol liquid and first residues, and transferring the first residues into a mixing tank;
4) Adding water to the first residue obtained in the step 4), wherein the ratio of the residue to the water is 1:1.05; centrifugal separation is carried out, the rotating speed of the centrifugal separation is 450r/min, and salt is separated out; distilling by a thin film evaporator to obtain fourth glycerol liquid and second residues;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding fructose, glycerol and propionic acid, wherein the mass fraction of the fructose is 10%, the mass fraction of the glycerol is 5%, and the mass fraction of the propionic acid is 5%; and simultaneously adding sulfur and iron metal biological modified carbon, wherein the mass fraction of the sulfur is 0.5%, and the mass fraction of the iron metal biological modified carbon is 0.05%, so as to obtain the composite carbon source.
Through experimental detection, the BOD5/COD ratio of the composite carbon source is about 0.81, and the composite carbon source can be directly applied to sewage treatment after dilution and has good denitrification promotion effect.
Example 7
In a sewage treatment station of a company in an electronic industry, the total nitrogen in the wastewater of a production line is higher because nitric acid is used in the production process. The total nitrogen of the influent water of the sewage treatment station is 200mg/L, the COD is 50mg/L, the biodegradability of the influent water COD is poor, and the denitrification by adding a carbon source is needed. Sodium acetate, glucose and the compound carbon sources of examples 3 and 6 are added into six pilot plant test devices using the company wastewater, and the water inflow rate of the pilot plant test devices is kept at 100m 3 /h。
Sodium acetate, glucose and the compound carbon sources of examples 3 and 6 are prepared into denitrifying carbon source solutions with the same COD equivalent concentration, and the six carbon sources are added according to the same volume, so that the flow of a dosing pump is kept consistent. The removal effect pair of the control group and the experimental group is shown in table 1.
Table 1 removal effect of comparative and experimental groups
According to the data, the composite carbon source can be used as a denitrification carbon source for sewage treatment, and compared with the carbon source in the prior art, the composite carbon source improves the nitrogen removal rate when COD with the same mass is added.
Meanwhile, the price of sodium acetate and glucose of the same type in the market is 4000-5000 yuan per ton, and the price of crude glycerol is less than 1000 yuan per ton.
Example 8
Water inflow rate of 50000m of industrial sewage treatment plant in Zhejiang 3 And/d, the COD concentration of the inlet water is 200mg/L, the total nitrogen concentration is 40mg/L, and the denitrification process is completed by adding an appropriate amount of carbon source due to insufficient C/N of the inlet water. Sodium acetate, glucose and the denitrified carbon source solutions of the same COD equivalent concentration as in examples 3 and 6 were prepared, and the six carbon sources were added in the same volume to maintain the same dosing pump flow, and the removal effect of the comparative and experimental groups was as shown in Table 2.
Table 2 comparison of removal effects of the comparison group and the experimental group
According to the data, the composite carbon source can be used as a denitrification carbon source for sewage treatment, and compared with the carbon source in the prior art, the composite carbon source can ensure that effluent of a sewage plant stably reaches the first-level A emission standard when COD with the same quality is added, and has good economy when the sewage plant is used on a large scale.
While the invention has been described with respect to preferred embodiments thereof, it will be understood by those skilled in the art that various modifications and additions may be made without departing from the scope of the invention. Equivalent embodiments of the present invention will be apparent to those skilled in the art having the benefit of the teachings disclosed herein, when considered in the light of the foregoing disclosure, and without departing from the spirit and scope of the invention; meanwhile, any equivalent changes, modifications and evolution of the above embodiments according to the essential technology of the present invention still fall within the scope of the technical solution of the present invention.

Claims (9)

1. The preparation method of the composite carbon source is characterized by comprising the following steps:
1) Mixing crude glycerol with acid, and performing acidification treatment to obtain first acidified oil and first glycerol;
2) Regulating the pH value of the first glycerol solution obtained in the step 1) to be 8.0-8.5, standing for layering, and removing the precipitate to obtain second glycerol solution;
3) Distilling the first acidified oil obtained in the step 1) under reduced pressure, and heating to obtain third glycerin solution and first residues;
4) Adding water into the first residue obtained in the step 3), centrifuging, evaporating and condensing to obtain fourth glycerol liquid and second residue;
5) Mixing the second glycerol solution obtained in the step 2) and the fourth glycerol solution obtained in the step 4), and adding saccharides, alcohols, acids and denitrification promoters to obtain the composite carbon source;
in step 1), the crude glycerol is derived from biodiesel by-products;
in the step 5), the denitrification promoter is sulfur and metal biological modified carbon, and the metal biological modified carbon is selected from any one of iron, magnesium, manganese and nickel;
the mass ratio of the sulfur to the composite carbon source is (0.5-1): 100;
the mass ratio of the metal biological modified carbon to the composite carbon source is (0.05-0.1): 100.
2. the method for producing a composite carbon source according to claim 1, characterized by comprising at least one of the following technical features:
11 In step 1), the acid is selected from one or more of formic acid, acetic acid, hydrochloric acid and sulfuric acid;
12 In step 1), adding acid to adjust the pH to 4.0-4.5;
13 In step 1), the acidification treatment time is 30-40min;
14 Step 1) further comprising transferring the first glycerol solution to a neutralization reactor.
3. The method for producing a composite carbon source according to claim 1, characterized by comprising at least one of the following technical features:
21 In the step 2), the reagent for adjusting the pH is an alkaline solution;
22 In the step 2), the second glycerol solution is subjected to impurity removal treatment.
4. The method for producing a composite carbon source according to claim 3, characterized by comprising at least one of the following technical features:
211 In feature 21), the alkaline solution is selected from barium hydroxide;
221 In feature 22), the method of removing impurities is: allowing the second glycerol solution to sequentially pass through a cation exchange column, an anion exchange column and an anion and cation exchange column.
5. The method for producing a composite carbon source according to claim 1, characterized by comprising at least one of the following technical features:
31 In the step 3), the vacuum degree of the reduced pressure distillation is controlled to be 0.15-0.17kPa;
32 Step 3), heating to 164-204 ℃;
33 In the step 3), the third glycerol liquid is refined glycerol;
34 In the step 3), the third glycerol solution is recycled.
6. The method for producing a composite carbon source according to claim 1, characterized by comprising at least one of the following technical features:
41 In step 4), the volume ratio of the first residue to the water is 1: (0.75-1.15);
42 In the step 4), the centrifugal separation device is a double-pushing centrifugal machine, and the rotating speed of the centrifugal separation is 450-550r/min;
43 In the step 4), the evaporation and condensation device is a thin film evaporator;
44 In step 4), the second residue is asphaltenes.
7. The method for producing a composite carbon source according to claim 1, characterized by comprising at least one of the following technical features:
51 In step 5), the saccharide is selected from one or more of glucose, galactose and fructose;
52 In step 5), the alcohol is selected from one or more of methanol, ethanol, glycol, glycerol and butanol;
53 Step 5), the acid is selected from one or more of acetic acid, propionic acid, n-butyric acid and isobutyric acid;
54 In step 5), the total mass of the second glycerol liquid and the fourth glycerol liquid is as follows: quality of saccharides: alcohol mass: acid mass= (60-70): (5-10): (5-10): (5-10).
8. A composite carbon source produced by the method for producing a composite carbon source according to any one of claims 1 to 7.
9. The use of a composite carbon source according to claim 8 for denitrification of wastewater.
CN202311227892.4A 2023-09-22 2023-09-22 Composite carbon source and preparation method and application thereof Active CN116969592B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311227892.4A CN116969592B (en) 2023-09-22 2023-09-22 Composite carbon source and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311227892.4A CN116969592B (en) 2023-09-22 2023-09-22 Composite carbon source and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN116969592A true CN116969592A (en) 2023-10-31
CN116969592B CN116969592B (en) 2024-01-05

Family

ID=88473364

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311227892.4A Active CN116969592B (en) 2023-09-22 2023-09-22 Composite carbon source and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN116969592B (en)

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101182281A (en) * 2007-12-18 2008-05-21 昆明理工大学 Method for refining biodiesel byproduct glycerin
CN106591398A (en) * 2017-01-23 2017-04-26 中国科学院合肥物质科学研究院 Method for obtaining SA by using biodiesel by-product crude glycerol to perform high added-value conversion
CN106660912A (en) * 2014-07-09 2017-05-10 普拉克生化公司 Process for manufacturing purified glycerol
WO2019039531A1 (en) * 2017-08-23 2019-02-28 バイオ燃料技研工業株式会社 Water treatment method, water treatment system, method for producing denitrifying agent, and apparatus for producing denitrifying agent
CN113443752A (en) * 2020-09-25 2021-09-28 青岛碧沃德生物科技有限公司 Soapstock recycling pollution-free process
CN114409065A (en) * 2021-12-30 2022-04-29 云南合续环境科技股份有限公司 Composite carbon source material and preparation method thereof
CN114772718A (en) * 2022-03-14 2022-07-22 南京信息工程大学 Production process of low-CN-ratio sewage biological denitrification plus novel composite carbon source
CN115745243A (en) * 2022-11-09 2023-03-07 淮安湛清生态环境材料有限公司 Method for producing composite carbon source by using byproduct gulonic acid mother liquor as substrate

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101182281A (en) * 2007-12-18 2008-05-21 昆明理工大学 Method for refining biodiesel byproduct glycerin
CN106660912A (en) * 2014-07-09 2017-05-10 普拉克生化公司 Process for manufacturing purified glycerol
CN106591398A (en) * 2017-01-23 2017-04-26 中国科学院合肥物质科学研究院 Method for obtaining SA by using biodiesel by-product crude glycerol to perform high added-value conversion
WO2019039531A1 (en) * 2017-08-23 2019-02-28 バイオ燃料技研工業株式会社 Water treatment method, water treatment system, method for producing denitrifying agent, and apparatus for producing denitrifying agent
CN113443752A (en) * 2020-09-25 2021-09-28 青岛碧沃德生物科技有限公司 Soapstock recycling pollution-free process
CN114409065A (en) * 2021-12-30 2022-04-29 云南合续环境科技股份有限公司 Composite carbon source material and preparation method thereof
CN114772718A (en) * 2022-03-14 2022-07-22 南京信息工程大学 Production process of low-CN-ratio sewage biological denitrification plus novel composite carbon source
CN115745243A (en) * 2022-11-09 2023-03-07 淮安湛清生态环境材料有限公司 Method for producing composite carbon source by using byproduct gulonic acid mother liquor as substrate

Also Published As

Publication number Publication date
CN116969592B (en) 2024-01-05

Similar Documents

Publication Publication Date Title
Gonzales et al. Enhancement of hydrogen production by optimization of pH adjustment and separation conditions following dilute acid pretreatment of lignocellulosic biomass
CN104099374B (en) A kind of rice straw alkali processes the method producing biogas with excess sludge mixture slaking
CN110734933B (en) Method for improving medium-chain fatty acid yield of anaerobic fermentation of waste activated sludge
CN113443752A (en) Soapstock recycling pollution-free process
CN113788537A (en) Low-C/N-ratio sewage biological denitrification composite carbon source and preparation method thereof
CN115385456B (en) Efficient denitrification sewage treatment agent and preparation method thereof
CN113666494A (en) Polyethylene glycol-containing sewage biological denitrification composite carbon source and preparation method thereof
CN114835250A (en) Process method for supplementing carbon source by SBR (sequencing batch reactor) by using kitchen waste phase change liquid
CN116969592B (en) Composite carbon source and preparation method and application thereof
CN101880115A (en) Method for supplementing denitrifying carbon source by utilizing excess sludge ethanol-type fermentation
CN113788536A (en) Production process of sewage biological denitrification composite carbon source with low C/N ratio
US3241943A (en) Method for the production of a fertilizer or soil improvement agent from sulfite waste liquor while recovering acids and combustible gases formed in the process
CN1176034C (en) Process and apparatus for urban refuse cite penetrating liquid by three stage plus one process
CN104529075A (en) Improved process for treating citric acid wastewater
CN109796022B (en) Method for producing poly-aluminum ferric silicate by using chlorosilane residual liquid, waste aluminum slag and acid sludge
CN103466791A (en) Improved pre-acidifying treatment process of citric acid wastewater
CN116251819A (en) Method for producing denitrifying carbon source for sewage treatment by utilizing organic waste residues in food industry
CN106277286B (en) Method for eliminating viscous swelling of activated sludge in biochemical system
CN112408592B (en) Composite carbon source for water treatment and preparation method and application thereof
CN114620900A (en) Denitrification treatment method for kitchen anaerobic wastewater
CN111115853A (en) Safe composite carbon source and production process thereof
CN114988581B (en) Composite carbon source with polymorphic functional flora growth promoting function and preparation and use methods thereof
CN114958930B (en) Method for preparing liquid carbon source by utilizing kitchen waste
CN110628836B (en) Method for improving sludge anaerobic fermentation production of short-chain fatty acid by using polyaluminum chloride
CN113772814B (en) Efficient multi-dimensional carbon source and preparation method 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
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20240218

Address after: No. 128 Xingfu North Road, Suqian City, Jiangsu Province, 223899

Patentee after: Jiangsu United Water Technology Co.,Ltd.

Country or region after: China

Patentee after: Shanghai boruisi Environmental Technology Co.,Ltd.

Address before: Room 577, No. 698, Lane 1588, Zhuguang Road, Qingpu District, Shanghai, 201702

Patentee before: Shanghai boruisi Environmental Technology Co.,Ltd.

Country or region before: China