After had been removed BOD and TSS, the amonia removal is required biologically. Are there problems to growing nitrifying bacteria for nitrification and difficult to settle it in sedimentation tank?
E. F. Latif, It is possible to grow nitrifyers in activated sludge and settle them. Compared to heterotrophs you use to remove BOD, nitrifyers grow slower and are more sensitive to pH and toxicity of the water.
Biological ammonia removal for secondary effluent wastewater is a well-established and widely used process in wastewater treatment. However, like any wastewater treatment method, it does come with certain challenges and potential problems.
Some of these issues include:
Nitrification rate: Nitrification is the biological process in which ammonia (NH3) is converted to nitrite (NO2-) and then to nitrate (NO3-). This process is carried out by nitrifying bacteria. Sometimes, the nitrification rate may not be as efficient as desired, leading to incomplete ammonia removal.
Temperature sensitivity: Nitrifying bacteria are temperature-sensitive, and their activity can be significantly affected by temperature fluctuations. Lower temperatures can slow down the nitrification process, leading to reduced ammonia removal rates in colder climates.
Toxicity: High concentrations of certain pollutants, such as heavy metals or certain chemicals, can inhibit the activity of nitrifying bacteria and hinder ammonia removal.
Seasonal variations: Changes in environmental conditions, particularly during heavy rain events or droughts, can affect the performance of biological processes like nitrification.
Sludge production: The nitrification process can result in the production of excess sludge, which needs to be managed and disposed of properly.
pH levels: Nitrification is sensitive to pH levels, and extreme pH values can disrupt the activity of nitrifying bacteria, affecting ammonia removal.
Hydraulic retention time (HRT): In some treatment systems, achieving the desired HRT can be challenging, impacting the efficiency of ammonia removal.
Ammonia spikes: In certain situations, sudden spikes in ammonia concentration can occur, which may overwhelm the nitrifying bacteria and lead to temporary inefficiencies in ammonia removal.
It's essential to note that ongoing research and advancements in wastewater treatment technologies may have addressed or improved some of these issues. Additionally, local factors and the specific design of the treatment system can influence the prevalence and significance of these challenges.
If you are involved in a wastewater treatment project or have specific concerns about ammonia removal, it's advisable to consult with wastewater treatment experts or professionals who are up-to-date with the latest developments and practices in the field.
Yes, there can be challenges and problems in biological ammonia removal for secondary effluent wastewater treatment. Ammonia removal is an essential step in wastewater treatment to reduce nitrogen levels, as excessive ammonia can cause environmental issues such as eutrophication and harm aquatic life. The biological removal of ammonia typically involves nitrification and denitrification processes carried out by specific groups of microorganisms. Here are some common problems and challenges associated with biological ammonia removal in secondary effluent wastewater treatment:
Nitrification Efficiency: Nitrification is the conversion of ammonia (NH4+) to nitrite (NO2-) and then to nitrate (NO3-). Achieving complete nitrification can be challenging, as it requires stable and efficient conditions for the growth and activity of nitrifying bacteria, such as Nitrosomonas and Nitrobacter.
Process Upsets: Nitrification can be sensitive to changes in environmental conditions, such as temperature fluctuations, pH variations, and toxic substances in the wastewater. Process upsets can lead to temporary inhibition or reduced nitrification efficiency.
Long Sludge Retention Time: Nitrifying bacteria typically have a longer sludge retention time (SRT) requirement compared to other microbial groups. This can limit the overall treatment capacity and may require larger reactor volumes for sufficient nitrification.
Denitrification Inhibition: Denitrification is the conversion of nitrate (NO3-) to nitrogen gas (N2) under anaerobic conditions. High dissolved oxygen levels or insufficient organic carbon in the secondary effluent can inhibit denitrification, reducing nitrogen removal efficiency.
Effluent Nitrate Concentration: Complete denitrification can lead to the production of nitrogen gas, which can be released to the atmosphere, or the incomplete denitrification may result in residual nitrate in the effluent. High nitrate concentrations in the effluent can still cause environmental issues.
Microbial Competition: In biological treatment systems, different microbial groups compete for resources. The presence of other nitrogen-transforming bacteria, such as anammox bacteria, may compete with nitrifiers and denitrifiers, affecting the overall ammonia removal efficiency.
Seasonal Variations: Seasonal changes in temperature, influent characteristics, and microbial activity can impact the performance of biological ammonia removal systems.
Energy Consumption: Biological ammonia removal processes often require aeration and mixing to maintain aerobic and anaerobic conditions, which can result in higher energy consumption compared to some physicochemical treatment methods.
Ammonia Fluctuations: In wastewater with variable ammonia concentrations, maintaining stable and consistent ammonia removal rates can be challenging.
To address these challenges, wastewater treatment plants may use process optimization, advanced process control, and innovative technologies such as bioaugmentation, enhanced process monitoring, and hybrid treatment approaches to achieve efficient biological ammonia removal. Careful design, operation, and maintenance are crucial to ensure reliable and effective nitrogen removal in secondary effluent wastewater treatment.