Case Study: Eliminating Foaming in Aeration Basins

Persistent foam on an aeration basin can look like a cosmetic nuisance, but it often signals a process imbalance. Excessive surface foam may indicate young or old sludge, filamentous organisms, high surfactant loading, poor return activated sludge control, or a combination of these conditions. If it reaches walkways, skimmer systems, or nearby drainage areas, it can also create housekeeping, odor, and compliance concerns.

This anonymized case study follows a 12-million-gallon-per-day municipal wastewater treatment plant in the Los Angeles Basin. Operators faced recurring tan and white foam across two biological treatment trains. The problem became most severe after wet-weather events and during periods of reduced influent strength.

The plant’s response demonstrates why foam control should begin with process diagnosis rather than repeated chemical spraying. By combining field observations, laboratory testing, solids inventory measurements, and targeted operational changes, the team reduced visible foam without installing new mechanical equipment.

The Problem Emerges

The first signs appeared as thin, stable patches near the effluent end of the aeration basins. Within several weeks, foam accumulated along basin walls and moved toward the secondary clarifiers. Operators initially applied a silicone-based antifoam during the morning shift, which produced short-term relief but did not prevent the foam from returning later in the day.

The two treatment trains did not behave identically. Train A developed dense, tan foam with a greasy appearance, while Train B showed lighter foam that dispersed more readily. Microscopic examination found abundant filamentous organisms in mixed liquor samples from Train A. Settleability also varied between samples, with sludge volume index readings increasing from a typical range near 110 mL/g to more than 170 mL/g.

The timing offered another clue. Foam increased after rainfall, when diluted influent and higher hydraulic flows changed the biological loading entering the facility. The operators reviewed stormwater flow impacts as part of the investigation, paying particular attention to infiltration, inflow, and industrial contributions during wet-weather periods.

Investigation Beyond Surface Symptoms

The team created a daily foam log rather than relying on informal observations. Each shift recorded foam color, thickness, location, odor, weather, basin dissolved oxygen, mixed liquor suspended solids, return activated sludge flow, and wasting volume. This made it possible to compare operating conditions on calm days with conditions during foam outbreaks.

Laboratory work focused on the conditions that support filamentous growth. Samples were examined under a microscope, and operators performed settleability tests at several points across both trains. The plant also reviewed influent biochemical oxygen demand, ammonia, alkalinity, and grease and oil results. No single parameter explained every event, but the pattern pointed toward low food-to-microorganism conditions combined with inconsistent solids age.

During wet-weather periods, influent flow rose quickly while organic loading increased only modestly. This reduced the effective food-to-microorganism ratio and shortened contact time in the primary process. At the same time, operators had been reducing wasting to conserve solids during low-load periods. The result was an older, more selectively retained biomass that favored filamentous organisms.

Testing the Likely Causes

Before changing the operating strategy, the plant established a baseline. The purpose was to separate causes that could be corrected through process control from those requiring source control or capital improvements.

Observation Likely Meaning Confirmation Method Initial Response
Stable tan foam Filamentous growth or surfactant accumulation Microscopy and influent review Adjust solids age and inspect upstream sources
High sludge volume index Poor settling and possible filament dominance Settleability testing Review wasting and return rates
Foam after rainfall Dilution, hydraulic shock, or sewer inflow Flow and rainfall correlation Track wet-weather loading
Low basin dissolved oxygen Selective conditions for certain filaments Continuous DO trend Balance air distribution
Rapid antifoam benefit followed by recurrence Symptom suppression without process correction Compare treated and untreated periods Limit chemical use to emergency control

Operators also checked whether air delivery was uneven across the basin. Several diffusers in Train A had reduced performance, creating localized low-oxygen zones even though the average basin dissolved oxygen appeared acceptable. This finding was important: an average reading can conceal biological conditions that exist near the basin floor or along individual air grids.

The team resisted making several large changes at once. Instead, it selected a sequence that could be measured: restore air distribution, establish a consistent solids inventory, increase observation frequency, and adjust return activated sludge flow based on clarifier blanket behavior rather than a fixed percentage of influent flow.

Corrective Actions In The Process

Maintenance staff cleaned and inspected the affected air grids, then verified airflow across the basin. Operators calibrated dissolved oxygen probes and added temporary sampling points near the inlet, middle, and outlet zones. These steps showed that the outlet end had adequate oxygen while the inlet zone periodically fell below the plant’s preferred operating range.

The plant then tightened control of wasting. Instead of making infrequent large-volume wasting adjustments, operators used smaller, scheduled changes based on mixed liquor concentration, clarifier performance, and estimated solids age. The objective was to move away from the excessively old sludge condition without causing a sudden loss of biological inventory.

Return activated sludge control also received attention. The operators reviewed return activated sludge control principles and began comparing return flow with blanket depth, settled sludge concentration, and clarifier effluent quality. This reduced the reliance on a fixed flow setting and helped maintain a more stable solids distribution through the secondary process.

Chemical antifoam was reserved for periods when foam threatened access routes or equipment. It was no longer treated as the primary solution. The plant also increased inspection of influent channels and screened materials for grease, cleaning agents, and other substances that could contribute to surface-active foam.

Results After Stabilization

Visible foam began to decline within two weeks of restoring air balance and normalizing wasting. By the sixth week, Train A generally showed only a narrow band of unstable foam along the basin edge, while Train B remained clear. The sludge volume index returned to approximately 120 to 135 mL/g, and secondary clarifier blanket levels became easier to predict.

The improvement did not come from a single operating setpoint. It came from reducing the conditions that allowed filamentous organisms to dominate. More uniform aeration removed low-oxygen pockets, consistent wasting moderated solids age, and responsive return sludge control prevented excessive accumulation in the clarifiers.

The team continued monitoring for three months. During two later rain events, hydraulic flow increased substantially, but foam remained manageable. Dissolved oxygen profiles were checked more often during wet weather, and operators temporarily increased sampling rather than automatically increasing air or applying antifoam.

The plant also documented the cost impact. Antifoam use fell by approximately 80 percent, while labor spent washing basin walkways declined. More importantly, the facility avoided carrying an unstable process into the cooler season, when settling and biological response can become more difficult to control.

Lessons For Water Professionals

Foam is a visible symptom, not a diagnosis. Its color, texture, persistence, location, and timing can help narrow the investigation, but operators need supporting data from microscopy, settleability testing, solids inventory calculations, and loading trends. A basin that looks adequately aerated at one monitoring point may still contain poorly mixed or oxygen-limited zones elsewhere.

The case also reinforces the value of disciplined records. The foam log connected field conditions with rainfall, flow, wasting, dissolved oxygen, and clarifier performance. Without that history, the plant might have continued changing chemicals or air rates without identifying the interaction between wet-weather dilution and solids age.

Technical competence grows when operators can discuss real process problems with peers, engineers, and agency staff. Programs that recognize practical achievement, such as the LABS Awards Banquet, help bring attention to the people who turn troubleshooting experience into better plant performance.

Actions That Support Lasting Foam Control

A durable response depends on making foam part of routine process control rather than treating it as an isolated nuisance. When operators connect surface observations with loading, aeration, solids management, and weather data, they can correct the underlying imbalance and preserve stable secondary treatment.

LABS of CWEA provides a practical setting for that exchange through technical presentations, facility tours, workshops, MOC certification courses, and automation training. Bring a foaming event, settling concern, or aeration challenge to a future professional discussion and help turn field experience into reliable water environment practice.