Amino benzene analog waste water biological treatment method
A biological treatment, waste water technology, applied in the direction of sustainable biological treatment, biological water/sewage treatment, water/sludge/sewage treatment, etc., can solve problems such as the inability to apply fluidized bed reactors, and achieve good economic benefits and environmental protection Benefits, waste reduction, and the effect of increasing the concentration of microorganisms
- Summary
- Abstract
- Description
- Claims
- Application Information
AI Technical Summary
Problems solved by technology
Method used
Examples
Embodiment 1
[0021] In the SBR reactor with an effective volume of 1.3L, large-porous cross-linked polystyrene white balls were used as immobilized microbial carriers. The carrier volume was 4% of the effective volume of the reactor. After 20-30 days of microbial immobilization, the synthetic A stable biofilm is formed on a macroporous polymer carrier. The test wastewater is simulated p-toluidine wastewater, whose pH value is adjusted to 5-10, and nitrogen and phosphorus nutrients are added to make the wastewater COD 1100mg / L and p-toluidine concentration 327mg / L. Add 0.8L waste water to the reactor in each batch, and the water inflow mode is instantaneous water inflow. At 25°C, when the aeration rate is 0.6L / min, after aeration for 360 minutes, sediment for 30 minutes and drain. The COD in the effluent is 10.5mg / L, the concentration of p-toluidine is less than 0.5mg / L, and the concentration of ammonia nitrogen is 20mg / L.
Embodiment 2
[0023] In the SBR reactor described in Example 1, macroporous cross-linked polystyrene white balls accounting for 6% of the effective volume were added as immobilized microorganism carriers. After 20-30 days of microorganism immobilization, a stable biofilm is formed on the synthetic macroporous polymer carrier. The test wastewater is simulated p-aminophenol production wastewater, whose pH value is adjusted to 5-10, and nitrogen and phosphorus nutrients are added to make the wastewater COD 2300mg / L and p-aminophenol concentration 648mg / L. The amount of water inflow and the way of water inflow are the same as in Example 1. At 15°C, when the aeration rate is 0.9L / min, after aeration for 420 minutes, sediment for 120 minutes and drain. The COD in the effluent was 16.4mg / L, the concentration of p-aminophenol was less than 0.5mg / L, and the concentration of ammonia nitrogen was 23.9mg / L.
Embodiment 3
[0025] In the SBR reactor described in Example 1, macroporous anion exchange resin D301 accounting for 10% of the effective volume was added as the immobilized microorganism carrier. After 20-30 days of microorganism immobilization, a stable biofilm is formed on the synthetic macroporous polymer carrier. Test waste water, water intake and water intake mode are the same as embodiment 1. At 10°C, when the aeration rate is 0.9L / min, after aeration for 480 minutes, sediment for 90 minutes and drain. The COD in the effluent is 17.1mg / L, the concentration of p-toluidine is less than 0.5mg / L, and the concentration of ammonia nitrogen is 24.1mg / L.
PUM
Abstract
Description
Claims
Application Information
- R&D Engineer
- R&D Manager
- IP Professional
- Industry Leading Data Capabilities
- Powerful AI technology
- Patent DNA Extraction
Browse by: Latest US Patents, China's latest patents, Technical Efficacy Thesaurus, Application Domain, Technology Topic, Popular Technical Reports.
© 2024 PatSnap. All rights reserved.Legal|Privacy policy|Modern Slavery Act Transparency Statement|Sitemap|About US| Contact US: help@patsnap.com