A kind of treatment method of cephalosporin antibiotic production wastewater

A technology for producing wastewater and treatment methods, which is applied in water/sewage treatment, water treatment parameter control, water/sewage multi-stage treatment, etc., can solve the problems of increasing treatment difficulty, iron-carbon fillers prone to hardening, and reduced crystallization efficiency, etc. Achieve the effect of avoiding sulfate accumulation, prolonging operation stability, and reducing the amount of condensed water

Active Publication Date: 2021-04-27
山东蓝然环境科技有限公司
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  • Application Information

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Problems solved by technology

[0002] Cephalosporin antibiotic production wastewater is a kind of organic pharmaceutical wastewater with complex components and high content, which contains lipids, alcohols, fermentation metabolites, mycelia and antibiotic residues and other refractory substances, and the wastewater also contains a large amount of sulfuric acid Ammonium, which makes it difficult to handle
[0003] At present, the methods to treat this kind of wastewater mainly include flocculation precipitation method, iron-carbon internal electrolysis method, advanced oxidation method, membrane separation technology and biological method. The above treatment methods have their own limitations. Synthesis of high-efficiency flocculants is still the current development direction; in the iron-carbon internal electrolysis method, the iron-carbon filler is prone to compaction, and the electrolysis efficiency is reduced; in the advanced oxidation method, the amount of oxidant required is large, the operating cost is high, and the economy is the whole project. Bottleneck, and produce chemical sludge; membrane separation technology is only used to remove residual antibiotic organic matter, membrane pollution control is difficult in the project, and the cleaning effect is not good; biological method: as a guarantee for the follow-up wastewater to meet the standard discharge, it must be pretreated to remove the residual antibiotics and high salt
In view of the limitations of the above methods, the combined process of concentration + evaporation crystallization + biochemical treatment is also a popular treatment method for high-salt wastewater. However, for pharmaceutical wastewater with complex components and high COD and ammonia nitrogen content, the treatment system is prone to serious damage. In addition, during the evaporation and crystallization process, due to the large temperature rise of the boiling point, the crystallization efficiency is reduced, which makes the continuous operation time of the system short, unstable or even unable to operate normally, and the treatment effect of organic matter and ammonia nitrogen is not good.

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  • A kind of treatment method of cephalosporin antibiotic production wastewater

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Embodiment 1

[0029] Processing method of the present invention comprises the following steps:

[0030] 1) Filtration: The raw water is filtered by the basket filter under the action of the raw water delivery pump and then enters the ultrafiltration device. The ultrafiltration device includes four ultrafilters connected in parallel to remove suspended solids and macromolecular organic matter in the raw water. The external pressure hollow fiber membrane is used in the ultrafiltration;

[0031] 2) Electrodialysis: Ultrafiltration effluent enters the first-level concentrated water tank and the first-level fresh water tank of the first-level electrodialysis to make up the liquid level, and the concentrated water of the first-level concentrated water tank and the fresh water of the first-level fresh water tank are transported through the pipeline To the inlet of the concentration chamber and the desalination chamber of the first-stage electrodialysis, set the voltage at 190~240V, and separate th...

Embodiment 2

[0035] The difference between this embodiment and Embodiment 1 is that: when the conductivity detector at the outlet of the first-stage electrodialysis concentrated water detects that the conductance of the concentrated water is higher than 160ms / cm, the concentrated concentrated water enters the concentrated concentrated water tank and then enters the MVR; When the conductivity detector at the fresh water outlet of the secondary electrodialysis detects that the conductivity of the fresh water is less than 6ms / cm, the fresh water enters the biochemical system.

Embodiment 3

[0037] The difference between this embodiment and embodiment 1 is that ammonia water is added to the concentrated concentrated water tank to adjust its pH to 6-7.

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Abstract

The invention discloses a method for treating waste water produced by cephalosporin antibiotics, which belongs to the field of waste water treatment. The present invention adopts the method of combining electrodialysis-MVR evaporation crystallization-A / O biochemical treatment, and controls the salt content of concentrated concentrated water and biochemical fresh water by adjusting the conductivity of the electrodialysis process, so that the salt and water in the raw water The dialysis device is fully separated, which improves the evaporation and crystallization efficiency of MVR, reduces the harm to microorganisms in the biochemical system, and improves the removal rate of organic matter and ammonia nitrogen. The pH of the concentrated concentrated water is kept at 6~8.5 to avoid the continuous enrichment of hydrogen ions in the MVR system and affect the boiling point temperature rise of ammonium sulfate and other salts, so that the MVR can continue to produce salt and prolong the stable operation time of the system.

Description

technical field [0001] The invention discloses a method for treating waste water produced by cephalosporin antibiotics, which belongs to the field of waste water treatment. Background technique [0002] Cephalosporin antibiotic production wastewater is a kind of organic pharmaceutical wastewater with complex components and high content, which contains lipids, alcohols, fermentation metabolites, mycelia and antibiotic residues and other refractory substances, and the wastewater also contains a large amount of sulfuric acid Ammonium, which increases the difficulty of its handling. [0003] At present, the methods to treat this kind of wastewater mainly include flocculation precipitation method, iron-carbon internal electrolysis method, advanced oxidation method, membrane separation technology and biological method. The above treatment methods have their own limitations. Synthesis of high-efficiency flocculants is still the current development direction; in the iron-carbon int...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C02F9/14
CPCC02F1/001C02F1/04C02F1/444C02F1/4693C02F3/30C02F9/00C02F2209/08C02F2209/14
Inventor 王磊
Owner 山东蓝然环境科技有限公司
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