CN109574309B - Method for reducing biotoxicity of antibiotic wastewater through membrane material - Google Patents
Method for reducing biotoxicity of antibiotic wastewater through membrane material Download PDFInfo
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- CN109574309B CN109574309B CN201811550810.9A CN201811550810A CN109574309B CN 109574309 B CN109574309 B CN 109574309B CN 201811550810 A CN201811550810 A CN 201811550810A CN 109574309 B CN109574309 B CN 109574309B
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
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- Engineering & Computer Science (AREA)
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Abstract
The invention belongs to the technical field of wastewater treatment, and particularly discloses a method for reducing biotoxicity of antibiotic wastewater through a membrane material, which comprises the following steps of (1) taking wastewater containing sludge, adding acid into the wastewater, and adjusting the PH of the wastewater to 3-4, (2) passing the wastewater in the step (1) through a filtering membrane, extruding the wastewater when the wastewater passes through the filtering membrane, adding alkali after the wastewater passes through the filtering membrane to adjust the PH of the wastewater to 7-8, and discharging the wastewater after the wastewater reaches the detection standard; (3) and (3) drying the sludge on the filtering membrane in the step (2) by using hot air, and removing the sludge on the filtering membrane. The invention is mainly used for treating wastewater, and solves the problem that the antibiotics are wrapped in the sludge and increase the environmental pollution along with the wastewater discharge.
Description
Technical Field
The invention belongs to the technical field of wastewater treatment, and particularly discloses a method for reducing biotoxicity of antibiotic wastewater through a membrane material.
Background
Antibiotics refer to a class of secondary metabolites with anti-pathogen or other activities generated by microorganisms (including bacteria, fungi, actinomycetes) or higher animals and plants during life, and chemical substances capable of interfering with other life cell development functions. Antibiotics commonly used in clinical practice include extracts from microbial cultures and chemically synthesized or semisynthetic compounds.
The antibiotic is prepared by fermenting, filtering and refining organic raw materials such as grains and the like through the vital activity of microorganisms by adopting a fermentation process, and has the characteristics of high COD (chemical oxygen demand) and ammonia nitrogen concentration, high chromaticity, high sulfate concentration, difficult biodegradation of contained pollutants, biotoxicity and the like in the process of producing the antibiotic. During the process of discharging the waste water, some antibiotics are wrapped in the sludge, and if the sludge is not filtered from the waste water, more antibiotics are discharged into the environment along with the waste water, so that the pollution to the environment is increased.
Disclosure of Invention
The invention aims to provide a method for reducing the biotoxicity of antibiotic wastewater through a membrane material, so as to solve the problem that the antibiotic is wrapped in sludge and increases the environmental pollution along with the discharge of the wastewater.
In order to achieve the purpose, the basic scheme of the invention is as follows: a method for reducing the biotoxicity of antibiotic wastewater by a membrane material, which comprises the following steps:
(1) taking wastewater containing sludge, adding acid into the wastewater, and adjusting the pH of the wastewater to 3-4;
(2) enabling the wastewater in the step (1) to pass through a filtering membrane, extruding the wastewater when the wastewater passes through the filtering membrane, adding alkali to adjust the pH value of the wastewater to 7-8 after the wastewater passes through the filtering membrane, and discharging the wastewater after the wastewater reaches the standard;
(3) and (3) drying the sludge on the filtering membrane in the step (2) by using hot air, and removing the sludge on the filtering membrane.
The working principle and the beneficial effects of the basic scheme are as follows:
(1) the method can inactivate part of antibiotics in the wastewater after adding the acid into the wastewater, and can generate precipitates at the same time, so that the sludge and the precipitates can be conveniently mixed together for cleaning;
(2) in the method, the sludge is air-dried by using hot air, so that the sludge is prevented from continuously remaining in the wastewater to influence the subsequent treatment of the wastewater;
(3) the method can effectively remove the sludge contained in the water, reduces the content of antibiotics in the water and reduces the pollution of the antibiotics to water resources.
Further, the acid added in the step (1) is one of sulfuric acid, nitric acid or hydrochloric acid. Partial antibiotics in the wastewater can be inactivated by adding acid, and heavy metal ions in the wastewater can be precipitated, so that the pollution of the wastewater to the environment is reduced.
Further, in the step (3), hot air is blown to the filtering membrane from the water outlet side of the filtering membrane, the sludge on the filtering membrane is dried by the hot air, and the dried sludge is blown away. After the sludge is dried, the sludge can form a sheet shape or a block shape, and the dried sludge is convenient to clean.
Further, stirring and heating are carried out during the process of adding the acid into the wastewater in the step (1). The wastewater is heated in the acid adding process so as to remove microorganisms in the water, and the pollution to the water body is reduced.
Further, the filtering membrane used in the step (2) is a filtering membrane made of polycarbonate, polyvinyl chloride, polyvinylidene fluoride, polysulfone, polyacrylonitrile, polyamide, polysulfone amide, sulfonated polysulfone, cross-linked polyvinyl alcohol or modified acrylic acid polymer material.
Drawings
FIG. 1 is a schematic structural diagram of an embodiment of the method for reducing the biotoxicity of antibiotic wastewater by using a membrane material.
Detailed Description
The following is further detailed by way of specific embodiments:
reference numerals in the drawings of the specification include: the filter cartridge comprises a filter cartridge 1, a sealing cover 2, a servo motor 3, a sleeve 4, a water inlet pipe 5, a first one-way valve 6, a discharge port 7, a water outlet 8, a through hole 9, a spiral groove 10, a slide hole 11, a top block 12, a spring 13, a horizontal pipe 14, an upper pipe 15, a lower pipe 16, a push plate 17, a water outlet pipe 18, a fourth one-way valve 19 and a frame 20.
In an embodiment, substantially as shown in figure 1, a method for reducing biotoxicity of antibiotic wastewater through a membrane material, comprising the steps of: (1) taking wastewater containing sludge, adding acid into the wastewater, and adjusting the pH of the wastewater to 3-4;
(2) enabling the wastewater in the step (1) to pass through a filtering membrane, extruding the wastewater when the wastewater passes through the filtering membrane, adding alkali to adjust the pH value of the wastewater to 7-8 after the wastewater passes through the filtering membrane, and discharging the wastewater after the wastewater reaches the standard;
(3) and (3) drying the sludge on the filtering membrane in the step (2) by using hot air, and removing the sludge on the filtering membrane.
When the processing steps are used, the filtering device comprises a rack 20, a filter cartridge 1 is installed on the rack 20, a sealing cover 2 is installed at the upper end of the filter cartridge 1, and a servo motor 3 with an output shaft arranged downwards is installed on the sealing cover 2. Install vertical sleeve 4 in the cartridge filter 1, the upper end of sleeve 4 and the lower extreme of sleeve 4 all with cartridge filter 1 inner wall seal weld. A cavity is formed between the outer wall of the sleeve 4 and the filter cartridge 1, a water inlet pipe 5 communicated with the interior of the sleeve 4 is installed on the left side of the upper portion of the filter cartridge 1, and a first one-way valve 6 communicated with the interior of the filter cartridge 1 in a one-way mode is installed in the water inlet pipe 5; the bottom of the filter cylinder 1 is provided with a discharge opening 7, and a fourth one-way valve 19 which is communicated outwards in one way is arranged in the discharge opening 7.
The inner wall of the sleeve 4 is provided with a spiral groove 10, a push plate 17 is connected in the spiral groove 10 in a sliding mode, and the upper end face of the push plate 17 is connected with an output shaft of the motor. A sealing ring is arranged on the contact surface of the push plate 17 and the spiral groove 10; through holes 9 are formed between the left side and the right side of the spiral groove 10 and the cavity, and the inner wall of each through hole 9 and the inner wall of the spiral groove 10 are in arc transition; the through hole 9 is internally provided with a membrane material for filtering sludge, and the membrane material is preferably an MBR membrane material. The push plate 17 is provided with a plurality of sliding holes 11 which are horizontally and uniformly distributed along the circumferential direction, a top block 12 is connected in each sliding hole 11 in a sliding mode, a spring 13 is connected between each top block 12 and the bottom of each sliding hole 11, and one end, close to the through hole 9, of each top block 12 is a cambered surface and can be abutted to the inner wall of the through hole 9 in a sealing mode.
A three-way pipe is arranged on one side, located in the cavity, of the through hole 9, the three-way pipe comprises a transverse pipe 14, an upper pipe 15 and a lower pipe 16 which are communicated with each other, a cleaning water pipe is connected onto the upper pipe 15, a blower is connected onto the cleaning water pipe, a heating wire is arranged in the blower, the lower end of the upper pipe 15 is connected to the position, close to the outer wall of the sleeve 4, of the transverse pipe 14, a second one-way valve conducting towards the interior of the sleeve 4 in a one-way mode is arranged in the upper pipe 15, and a third one-way valve conducting towards the interior of the cavity in a one-way mode is arranged in the lower pipe 16; the lower part of the cavity structure is provided with a water outlet 8, and a water outlet pipe 18 is arranged at the water outlet 8.
Before the filtering device is used for filtering the waste water, the push plate 17 is positioned at the bottom of the sleeve 4; the waste water is flushed into the sleeve 4 through the water inlet pipe 5, the servo motor 3 is started, the servo motor 3 rotates to drive the push plate 17 to rotate, the push plate 17 rotates to move upwards along the spiral groove 10, the first one-way valve 6 is in a closed state in the upward movement process of the push plate 17, the push plate 17 moves upwards to extrude the waste water, the waste water enters the transverse pipe 14 through the membrane material and the through hole 9 after being extruded, and the waste water enters the cavity through the third one-way valve and the lower pipe 16; after waste water passes through the membrane material, the sludge contained in the waste water is filtered on the membrane material, the top block 12 rotates along with the push plate 17, the top block 12 slides into the through hole 9 to extrude the water in the through hole 9 into the transverse pipe 14, and meanwhile, the top block 12 extrudes the sludge on the filtering membrane and enables the sludge to be adhered on the membrane. Because push pedal 17 and sleeve 4 inner wall rotate sealing connection, consequently, push pedal 17 moves the back upwards, and the position that sleeve 4 is located the push pedal 17 below is the negative pressure, and the third check valve closes, and the second check valve is opened, and the clear water that washs in the water pipe enters into violently managing 14 in, along with push pedal 17 moves upwards, washs in the water pipe hot-blast entering sleeve 4, and at this in-process, hot-blast mud with the membrane material weathers and blows off the membrane material.
When the push plate 17 moves to the upper part of the sleeve 4, the waste water in the sleeve 4 is completely discharged; the servo motor 3 is controlled to rotate reversely and drive the push plate 17 to rotate reversely, the push plate 17 drives the ejector block 12 to move in the spiral groove 10 in the reverse rotating process, the dry sludge in the spiral groove 10 is pushed out of the spiral groove 10 when the push plate 17 rotates, meanwhile, the fourth one-way valve 19 is opened, and the push plate 17 moves downwards to discharge the sludge below the push plate 17 through the discharge port 7.
The foregoing is merely an example of the present invention and common general knowledge of known specific structures and features of the embodiments is not described herein in any greater detail. It should be noted that, for those skilled in the art, without departing from the structure of the present invention, several changes and modifications can be made, which should also be regarded as the protection scope of the present invention, and these will not affect the effect of the implementation of the present invention and the practicability of the patent.
Claims (5)
1. A method for reducing the biotoxicity of antibiotic wastewater by a membrane material is characterized by comprising the following steps:
(1) taking wastewater containing sludge, adding acid into the wastewater, and adjusting the pH of the wastewater to 3-4;
(2) enabling the wastewater in the step (1) to pass through a filtering membrane, extruding the wastewater when the wastewater passes through the filtering membrane, adding alkali to adjust the pH value of the wastewater to 7-8 after the wastewater passes through the filtering membrane, and discharging the wastewater after the wastewater reaches the standard;
(3) drying the sludge on the filtering membrane in the step (2) by using hot air, and removing the sludge on the filtering membrane;
when the filtering device is used, the filtering device comprises a frame, a filtering cylinder is arranged on the frame, a sealing cover is arranged at the upper end of the filtering cylinder, and a servo motor with an output shaft arranged downwards is arranged on the sealing cover; a vertical sleeve is arranged in the filter cylinder, and the upper end of the sleeve and the lower end of the sleeve are hermetically welded with the inner wall of the filter cylinder; a cavity is formed between the outer wall of the sleeve and the filter cartridge, a water inlet pipe communicated with the interior of the sleeve is installed on the left side of the upper portion of the filter cartridge, and a first one-way valve communicated with the interior of the filter cartridge in a one-way mode is installed in the water inlet pipe; a discharge outlet is formed in the bottom of the filter cylinder, and a fourth one-way valve which is communicated outwards in one way is installed in the discharge outlet;
the inner wall of the sleeve is provided with a spiral groove, a push plate is connected in the spiral groove in a sliding manner, and the upper end surface of the push plate is connected with an output shaft of the motor; a sealing ring is arranged on the contact surface of the push plate and the spiral groove; through holes are arranged between the left side and the right side of the spiral groove and the cavity, and the inner wall of the through hole and the inner wall of the spiral groove are in arc transition; a membrane material for filtering sludge is arranged in the through hole, a plurality of sliding holes which are horizontally and uniformly distributed are formed in the push plate along the circumferential direction, a top block is connected in the sliding holes in a sliding mode, a spring is connected between the top block and the bottom of the sliding hole, and one end, close to the through hole, of the top block is a cambered surface and can be in sealing abutting joint with the inner wall of the through hole;
a three-way pipe is arranged on one side of the through hole, which is positioned in the cavity, and comprises a transverse pipe, an upper pipe and a lower pipe which are mutually communicated, a cleaning water pipe is connected onto the upper pipe, a blower is connected onto the cleaning water pipe, a heating wire is arranged in the blower, the lower end of the upper pipe is connected onto the position, which is close to the outer wall of the sleeve, of the transverse pipe, a second one-way valve which is in one-way conduction towards the interior of the sleeve is arranged in the upper pipe, and a third one-way valve which is in one-way conduction towards the interior of the cavity is arranged in the lower pipe; the lower part of the cavity structure is provided with a water outlet, and the water outlet is provided with a water outlet pipe.
2. The method for reducing the biotoxicity of the antibiotic wastewater through the membrane material as claimed in claim 1, wherein the acid added in the step (1) is one of sulfuric acid, nitric acid or hydrochloric acid.
3. The method for reducing the biotoxicity of the antibiotic wastewater through the membrane material as claimed in claim 1, wherein in the step (3), hot air is blown to the filtering membrane from the water outlet side of the filtering membrane, the hot air blows the sludge on the filtering membrane and blows the dried sludge away.
4. A method for reducing the biotoxicity of antibiotic wastewater through a membrane material according to any one of claims 1 to 3, wherein the step (1) of adding acid to wastewater is carried out by stirring and heating.
5. The method for reducing the biotoxicity of the antibiotic wastewater through the membrane material as claimed in claim 4, wherein the filtering membrane used in the step (2) is a filtering membrane of polycarbonate, polyvinyl chloride, polyvinylidene fluoride, polysulfone, polyacrylonitrile, polyamide, polysulfone amide, sulfonated polysulfone, cross-linked polyvinyl alcohol or modified acrylic acid polymer material.
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Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
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CN103344715A (en) * | 2013-06-20 | 2013-10-09 | 中国环境科学研究院 | Method for separation and enrichment of penicillin antibiotics in water |
CN103450477A (en) * | 2012-05-31 | 2013-12-18 | 海洋王照明科技股份有限公司 | Preparation method of graphene composite current collector |
CN106986433A (en) * | 2017-04-20 | 2017-07-28 | 中国科学院生态环境研究中心 | The preprocess method and antibiotic pharmaceutical wastewater processing method of antibiotic in a kind of removal antibiotic pharmaceutical wastewater |
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Publication number | Priority date | Publication date | Assignee | Title |
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CN103450477A (en) * | 2012-05-31 | 2013-12-18 | 海洋王照明科技股份有限公司 | Preparation method of graphene composite current collector |
CN103344715A (en) * | 2013-06-20 | 2013-10-09 | 中国环境科学研究院 | Method for separation and enrichment of penicillin antibiotics in water |
CN106986433A (en) * | 2017-04-20 | 2017-07-28 | 中国科学院生态环境研究中心 | The preprocess method and antibiotic pharmaceutical wastewater processing method of antibiotic in a kind of removal antibiotic pharmaceutical wastewater |
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