Sludge Bulking vs. Sludge Settling Ways to improve wastewater treatment in India
Sludge Bulking vs Settling: Biotech Companies in India

“Our MLSS is quite high, but we are not getting enough settling. “ or “Our biomass development is very good as our MLSS is high, but we have very little BOD/COD reduction”. these statements are often given by EHS managers. However, the concept of MLSS is completely misunderstood; it’s never the quantity of MLSS, it’s always the quality of MLSS. The settling of sludge and BOD reduction always correspond with how good the MLSS is, and not how much it is.

This blog intricately explains the difference between sludge bulking and sludge settling, and which factors are necessary to look out for.

Sludge Settling vs Sludge Bulking:

With the growing awareness of operational efficiency, several biotech companies in India are now addressing sludge bulking challenges through microbial innovation and advanced diagnostics.

Healthy Sludge Settling:

In a well-operating secondary clarifier, biomass flocs are compact, dense, and settle rapidly. The supernatant above appears clear, and the sludge blanket remains stable.

Sludge Bulking:

Here, the sludge appears fluffy, loose, and struggles to compact at the bottom. The supernatant turns turbid, and sludge blankets may rise or disperse.

Parameter Healthy Settling Sludge Bulking
SVI (Sludge Volume Index) 80–120 mL/g >150 mL/g
Sludge appearance Dense, compact flocs Loose, filamentous flocs
Supernatant Clear Turbid
Settling time 20–30 mins >45 mins
Cause Balanced system Filamentous overgrowth, F/M imbalance
Why Good MLSS ≠ Good Settling

Operators often celebrate high MLSS as a sign of strong microbial population. But MLSS is a mass reading-It doesn’t distinguish between healthy floc-formers and problem-causing filamentous organisms.

“ Think of it like body weight: Two individuals weigh the same, but one may be with lean muscle, the other with excessive fat.

In bulking scenarios, the bulk of MLSS is held together by filamentous bacteria-these long, thread-like organisms stretch out of flocs, creating open, web-like structures that trap water and resist compaction.

Reliable biocultures companies have been instrumental in developing floc-forming microbial strains specifically tailored for bulking control.

What Causes Sludge Bulking?
  1. Filamentous Bacteria Overgrowth

Common species: Type 021N, Sphaerotilus, Microthrix parvicella, Thiothrix

These bacteria thrive under specific conditions such as:

Low DO (<1.0 mg/l) – especially at floc centers.

High F/M ratios – excess food leads to dominance of fast-growing filaments

Nutrient Imbalance– N and P deficiency affect floc formation

Surfactants and FOG – common in food, dairy, and textile industries

Hydraulic surges – shock loading from upstream process

Leading microbial companies in India are providing industry-specific solutions for complex ETP issues, helping clients achieve consistent results in variable conditions.

 

  1. F/M Ratio Imbalance

Too much organic load relative to MLSS results in excessive microbial growth, and filamentous bacteria often outcompete floc-formers.

Ideal F/M ratio: 0.2-0.5 kg BOD/kg MLSS/day

Bulking is more likely when F/M > 0.6 or < 0.1, especially during inconsistent feed conditions.

  1. pH and Toxic Shocks

Sudden changes in pH (below 6.5 or above 8.5) , or toxic loads (solvents, phenols, metals) can kill floc-formers and allow filaments to dominate during regrowth. However, Solutions like those from Team One Biotech, a known player among bioculture for ETP STP plant manufacturers, are reshaping how industries manage MLSS health and sludge behavior.

 

Decoding SVI and other key Indicators

Sludge Volume Index (SVI) is the gold standard for assessing settleability.

  • SVI = ( Settled sludge volume in 30 mins, mL/L) / MLSS (g/L)
  • SVI < 100 = Good settling
  • SVI 120–150 → Early warning of bulking
  • SVI > 200 → Severe bulking

Other red flags:

  • Rising sludge in the clarifier
  • Scum layer formation
  • Poor TSS in final discharge
  • Varying DO and pH patterns in aeration tanks
Countermeasures- How to fix Bulking?

In addition to microbial solutions, industrial odor control systems  also play a pivotal role in overall ETP performance and workplace hygiene.

Short-Term Fixes:

  • Chlorination or Peracetic Acid Dosing: Targets filamentous bacteria selectively. Start with 0.5–1 ppm, monitor response.
  • Increase DO Levels: Maintain >2.0 mg/L throughout the aeration tank, especially in large tanks or tanks with dead zones.
  • Sludge Wasting: Reduce SRT (sludge retention time) to control filament growth. Remove excess MLSS.
  • Polymers in Clarifier: For emergency clarity issues, short-term use of cationic polymers can compact sludge.

Long-Term Solutions:

  • Nutrient Balancing: Maintain COD:N:P at approx. 100:5:1. Add urea or DAP if needed.
  • Equalization Tank: Smooth out hydraulic/organic loading rates to the aeration tank.
  • Bioculture Regeneration: Consider seeding with robust floc-forming consortia after bulking episodes.
  • Upgrade Aeration: Switch to fine-bubble diffused aeration systems to improve oxygen transfer.
  • Micronutrient Support: Trace metals like iron, cobalt, and molybdenum support healthy floc formers.

If you’re exploring biocultures for ETP plant manufacturers in India or need effective bacteria solutions for wastewater treatment, Team One Biotech offers proven blends tested across sectors.

Conclusion:

Remember one quote: What settles well, treats well. MLSS and BOD tell only one part of the story – settleability, floc health, and microbial balance complete the picture.

As experts and EHS leaders, we must look beyond the dashboard. A 3500 mg/L MLSS might impress, but if your sludge floats and supernatant clouds, your ETP is already sending you a warning.

Looking for a trusted waste water treatment company to resolve sludge settling problems? Contact Team One Biotech today for tailored solutions and microbial consultation.

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Anaerobic Wastewater Treatment: Demystifying Methanogenesis
Anaerobic Wastewater Treatment: Demystifying Methanogenesis

The wastewater treatment world is an unending sea of types of processes and variations. One such process, the anaerobic treatment, holds a prominent and popular reputation due to its low CAPEX-OPEX and generation of byproducts such as methane, which is valuable as well as a clean energy source.

The process that leads to methane production is known as methanogenesis-which is the final and slowest step in the anaerobic digestion chain, where intermediate acids and hydrogen are converted into methane.

However, the process is mostly underperforming in the industries due to its bottlenecks and variable mechanism. This blog helps readers understand the intricacies of methanogenesis and helps understand the concept and mechanism.

In the rapidly evolving landscape of anaerobic wastewater treatment, industries are recognizing the limitations of traditional systems and turning toward advanced, high-efficiency strategies. With increasing load from industrial effluent treatment, especially containing high COD and toxic compounds, the need for anaerobic bioreactor optimization is more critical than ever.

With the increasing demand for bacteria solutions for wastewater treatment, industries are actively seeking partners who understand both biology and process engineering.

Companies like Team One Biotech lead the way among bioculture companies and microbial companies in India, delivering high-performance strains suited for industrial ETPs.

We provide expert consulting and microbial formulations tailored for anaerobic systems. Contact us today to learn more about our solutions and transform your treatment process.

What is Methanogenesis?

Methanogenesis is the last step in anaerobic digestion, where the end products from acetogenesis and acedogenesis process are converted into methane gas and CO2 by methanogenic archaea.

Modern facilities strive for not just compliance but profitability through biogas production efficiency, transforming waste streams into energy assets. The use of engineered microbial consortia, such as T1B Anaerobio, ensures higher methane recovery from wastewater even under challenging conditions like salinity and shock loads.

Core stages of Anaerobic Digestion:

  1. Hydrolysis: Breakdown of complex organics (proteins, carbs, Fats)
  2. Acidogenesis: Fermentation into VFAs (volatile fatty acids), alcohol, H2.
  3. Acetogenesis: Conversion of VFAs into acetate, H2, and CO2.
  4. Methanogenesis: Final step producing CH4 and CO2.

Types of methanogens:

Pathway Microbial Group Substrate
Acetoclastic Methanosaeta, Methanosarcina Acetate → CH₄ + CO₂
Hydrogenotrophic Methanobacterium, Methanococcus H₂ + CO₂ → CH₄

 

These microbes are obligate anaerobes, extremely sensitive to environmental shifts-and incredibly slow-growing.

Why does methanogenesis often fail?

As evident, it is important to have success in all three processes i.e. Hydrolysis, Acidogenesis, and Acetogeneis, before Methanogenesis  to succeed. This requires proper management of pH, temperature, HRT and induction of right biomass. However, in most cases all the three preceding processes are comparatively easier to get executed, it is this methanogenetic process only where most plants struggle due to:

  1. Acid accumulation/VFA Buildup
  • Acidogenesis is rapid, while methanogenesis is slow.
  • Result: VFA overload, which causes pH to drop below 6.8—a toxic zone for methanogens.

 

  1. Toxic Inhibitors

Common industrial effluents contain:

  • Heavy metals (Zn, Cu, Cr)
  • Sulfides
  • Phenols
  • Ammonia >2000 mg/L

These compounds directly inhibit methanogenic enzyme systems.

  1. Salinity and TDS stress

TDS above 15000-20000 ppm imposes osmotic stress, especially on Methanosaeta, which is already slow-growing.

 

  1. Lack of Granular Structure in Reactors

Granules in the sludge allow the methanogens to thrive in micro-environments.

  • Poor granulation = less protection = washout
How to Improve Methanogenesis- Practical Strategies

Improving methanogenesis requires a holistic approach involving operational tuning, microbial reinforcement, and environmental stability.

  1. Maintain Optimal pH: 6.8 – 7.4

Methanogens are extremely pH sensitive; any fluctuation can halt the methanogenic process that leads to unwanted reverses.

  1. Control Organic Loading Rate (OLR)

Gradually ramp up OLR during commissioning, ideal OLR: 1.5-3.5 kg COD/m3/day for stable systems. Overfeeding typically leads to acid overload and ultimately methanogen collapse.

  1. Ensure Adequate Retention Time

The ideal HRT should be between 8-15 days (depending on the substrate). The SRT should be even longer in high-loading systems.

  1. Use advanced Biocultures enriched in Methanogens

Key Traits of Effective Methanogenic Biocultures:

  • Contains both acetoclastic and hydrogenotrophic strains
  • High cell viability in anaerobic, low-oxygen environments
  • Pre-adapted to shock loads, high COD, and salinity

At Team One Biotech, our T1B Anaerobio blend includes halotolerant Methanobacterium and facultative syntrophic partners that stabilize early acid-phase products and prevent VFA accumulation.

  1. Add Conductive Materials (Bio-Stimulation)
  • Use activated carbon, biochar, or magnetite in digesters.
  • These promote direct interspecies electron transfer (DIET), bypassing slower H2 pathways
  • Result: Faster methanogenesis and increased CH4 yield
  1. Control Sulfates and Heavy Metals

 Sulfate-reducing bacteria (SRB) compete with methanogens for substrate.

  • High sulfide also directly poisons methanogens
Key Indicators of Methanogenesis Health
Parameter Healthy Range
pH 6.8 – 7.4
VFA/Alkalinity ratio <0.3
ORP -300 to -400 mV
Biogas CH₄ content >60%
Foaming Minimal (indicates balance)
Gas production rate Steady increase or plateau
Methanogenesis is Fragile, but Fixable

Methanogenesis is the most sensitive yet rewarding step in anaerobic treatment. It’s where the “waste” becomes “resource,” and the environmental liability transforms into a clean, combustible asset.

But to get there, industries must move beyond legacy systems and general-purpose biology.

They must:

  • Understand the microbial bottlenecks
  • Deploy engineered or acclimated methanogens
  • Support them with pH buffering, controlled feeding, and granular retention

Only then can your anaerobic system realize its full potential — both in COD removal efficiency and renewable methane production.

Conclusion:

Achieving high COD removal technology performance depends heavily on maintaining organic loading rate control, optimal pH, and reducing VFA accumulation. Furthermore, granular sludge formation enhances microbial retention and process stability, which is vital in high-strength wastewater treatment systems.

Through targeted bioaugmentation for anaerobic digestion, enriched with salinity resistant methanogens, it’s now possible to manage volatile environments and optimize yield. These microbial consortium for ETP solutions include both acetoclastic and hydrogenotrophic archaea, enabling efficient conversion pathways and reduced inhibition.

One promising method includes introducing conductive material in digesters, which boosts DIET and facilitates faster VFA to methane conversion. This, combined with proper HRT/SRT balance and T1B Anaerobio application, unlocks new levels of process performance.

As we progress towards zero-waste water solutions and advanced ETP solutions, methanogenesis is no longer just a biological reaction—it’s a cornerstone of sustainable industrial practice.

In recent years, several biotech companies in India have made significant strides in anaerobic treatment technologies, offering customized microbial formulations.

Team One Biotech is one of the leading Biotech Companies in India, providing advanced microbial solutions like bacteria for ETP treatment and bacteria culture for wastewater treatment.
???? Reach out now to enhance your wastewater treatment efficiency.

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industrial holidays Anaerobic Wastewater Treatment in Industries
The effect of industrial holidays on ETP health

The ecosystem of industries is complex as well as consistent. However, shutdowns due to festivals, season, operational failure, or force give a halt to the whole system. Although mostly planned, these industrial holidays are intended to give relief, but deep down in the concrete basins of effluent treatment plants brews a storm of crisis, whether it may be in the primary, secondary, or tertiary systems.

Looking for expert solutions to manage ETP shutdown challenges? Contact Us today for tailored advice and services!

And if we focus on the secondary system, the microbial population gets the worst hit. This blog focuses on what happens inside the secondary system during an industrial holidays, its effects, precautions, and prevention.

The living Microbial world of ETP:

The secondary system is like a society where microbial populations i.e, bacteria, fungi, yeast, metazoans etc. thrive on:

Food: Readily biodegradable organic matter.

Shelter: Biofilms, flocs, or suspended habitats.

Environmental Comfort: pH, temperature, DO, and nutrients in a narrow optimal range.

Maintaining microbial diversity and stability is crucial for consistent ETP performance.

Microbial Starvation- A Hidden Shutdown Crisis

A 10-15 day shutdown without influent feed creates what we call a starvation phase in the bioreactor. The period can trigger several microbial stress responses:

Autolysis Begins:
  • Without food, heterotrophic bacteria begin digesting their own cellular reserves.
  • When reserves run out, cell walls rupture, releasing intracellular enzymes and ammonia into the mixed liquor.
Shift in Community Structure:
  • Fast-growing, high-COD degraders die off first.
  • Resilient microbes like filamentous bacteria and nitrifiers may survive longer, but their metabolic activity drops drastically.
Dissolved Oxygen (DO) Becomes Redundant:


  • With no substrate to oxidize, aeration continues but becomes wasteful.
  • High DO levels can paradoxically stress certain facultative anaerobes used to fluctuating oxygen levels.


MLSS/MLVSS Decline:
  • The Mixed Liquor Volatile Suspended Solids (MLVSS)- the biologically active portion of MLSS drops due to decay.
  • Settling characteristics deteriorate, and the SVI (Sludge Volume Index) can spike due to deflocculation.
Recovery is Not Instant – The Myth of “Rest and Run”

When production resumes, many assume the ETP will bounce back like a machine switched on. But biological wastewater treatment systems have no reset button.

Lag Phase in COD Reduction
  • Microbial populations take time to rebuild numbers and enzyme systems.
  • Expect 2-5 days of poor performance and higher COD/BOD in the outlet, especially in systems with no pre-seeding plan.
Sludge Age Misbalance
  • Sludge that has aged during the shutdown may have lost its settling efficiency.
  • Decayed sludge may also release toxins and nutrients, creating internal loading.
Shock Loads on Restart
  • Sudden reintroduction of full-strength effluent can lead to shock loading.
  • This exacerbates foaming, odor, and even system upset.
Preventive Measures

ETP health during shutdowns doesn’t have to be a gamble. Here are proven strategies, drawn from both research and field practices.

1.Feed Synthetic System:
  • Use glucose, molasses, milk whey, or diluted Urea/COD substitutes to mimic organic load at low levels (10-20% of actual COD).
  • Feed once or twice daily to maintain microbial respiration and floc integrity.\
2.Aerate intermittently:
  • Continuous aeration is wasteful. Instead, apply 4-6 hours/day intermittent aeration to maintain DO and prevent anoxic.
3.Monitor pH and ORP
  • During starvation, microbial metabolism can skew pH or ORP. Keep these in range to avoid unfavorable drift.
4.Bioaugmentation on Restart
  • Introduce high-count commercial biocultures tailored to your effluent type. This accelerates recovery.
  • Use starter cultures or preserved sludge from pre-holiday if available.
5.Sludge Management 
  • Remove aged or decaying sludge before shutdown. 
  • During long holidays, periodic recirculation or RAS/WAS adjustments prevent septic conditions.
Maintaining ETP Efficiency During Industrial Holidays with Bioculture Support

When industrial units pause operations during holidays, the ETP treatment process often slows down due to the absence of organic load. Microbes inside the aeration tank gradually lose activity, leading to poor degradation once the plant restarts. That’s where a bioculture for ETP operations becomes critical — it revitalizes the microbial community, improves resilience, and stabilizes performance without costly chemical interventions.

During downtime, parameters like ETP sludge volume, dissolved oxygen, and pH can fluctuate drastically. A pre-dosage of selected microbial strains helps maintain a balanced environment and prevents sludge bulking or odour generation. When operations resume, the system achieves faster recovery and reduced start-up lag.

To ensure long-term system reliability, work with trusted ETP plant manufacturers in India who understand the importance of integrating biological solutions into design. Many modern ETP and STP systems now include dedicated dosing points for microbial formulations and smart monitoring dashboards that track ETP standard parameters such as BOD, COD, TSS, and MLSS.

Whether you operate a textile, chemical, or food processing unit, maintaining your ETP treatment plant during holidays means safeguarding compliance and avoiding post-shutdown surges in effluent load. Explore how Team One Biotech’s Bioculture Solutions ensure consistent ETP water treatment efficiency even under variable operating conditions.

For more insights on biological treatment technologies, check out our detailed blog on What Are Biocultures for Wastewater Treatment — A Complete EHS Guide and a practical case study Bioculture for ETP- How a Textile Unit Stabilized ETP Performance with T1B Aerobio . Both resources complement this article by showing how bioculture for ETP transforms operational challenges into measurable efficiency gains.

Conclusion:

Industrial holidays are an unavoidable part of operations across industries such as textiles, pharmaceuticals, and chemicals and can’t be avoided but the problems related to it in an ETP can surely be avoided by taking the right steps, proper planning, and taking proactive measures.Investing in bioaugmentation, sludge handling, and strategic aeration ensures microbial resilience during shutdowns.

Team One Biotech is one of the leading Biotech Companies in India, providing advanced microbial solutions like bacteria for ETP treatment and bacteria culture for wastewater treatment.
Reach out now to enhance your wastewater treatment efficiency.

Email: sales@teamonebiotech.com

Visit: www.teamonebiotech.com

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Replacing Urea-DAP in a Textile Industry
Introduction:

We, at Team One Biotech LLP, help industries achieve sustainability goals with our biological wastewater treatment solutions, offering natural replacements for chemicals like urea-DAP and other nutrients.

In this success story, we are going to walk through the treatment efficiency and results achieved using SustainX for a leading textile company located at Dabhasa, GIDC, Gujarat. If you want to know more, feel free to contact us. 

The industry happens to be one of the most compliant and efficient in terms of textile wastewater treatment, they had a very good ETP mechanism and trained staff. However, they had a huge consumption of UREA-DAP, leading to high OPEX, also they used to experience sudden spikes in Ammoniacal nitrogen values during winters.

ETP Flow chart:

Primary- Biological and Tertiary systems, with RO & MEE. The activated sludge process (ASP) has 3 aeration tanks in series and one anoxic tank before the aeration tanks. 

Flow:1500 m3/day
Inlet COD:8,000 to 12,000 ppm
Inlet Ammoniacal Nitrogen:280 to 320 ppm
COD outlet after biological treatment:  1800 to 2500 ppm
Ammoniacal Nitrogen after biological treatmeent120 to 170 ppmDuring Spike: 200-250 ppm
Urea – DAP consumption800 kgs/day – 400 kgs/day respectively
Challenges:

Why traditional nutrients are inefficient in ETPS:

The commonly used urea and DAP are often overused in industrial treatment plants and they limit bioavailability for microbes. This results in poor nutrient uptake in biomass and limitations in COD and nitrogen removal causing ammonia spikes disturbing overall textile wastewater treatment systems.

1.The F/M ratio was low due to heavy consumption of UREA-DAP, leading to higher OPEX.

2.Sudden spike in ammoniacal nitrogen levels, especially in winters, due to non-consumption of ammonia from these fertilizers.

3.Saturation in COD is degrading efficiency.

The Scrutiny:

After a complete study of the plant through our WWTP evaluation form, on-site visits, and discussions with the EHS team, we concluded:

1.The F/M ratio gets lower if we stop urea-DAP addition.

2.The spike in ammoniacal nitrogen was due to the higher concentration of non-available nitrogen in the aeration tank, which was not absorbed by the biomass.

3.The indigenous microbial population was only performing at 60% efficiency in terms of COD reduction due to lower nutrient absorption despite a heavier dosage of UREA-DAP.

The Approach:

How T1B SustainX Works Better Than Urea-DAP:

SustainX is enriched with the naturally derived formulations comprising organic carbon and essential nutrients. It accelerates microbial metabolism and enhances organic waste degradation. Its unique formula helps eliminate side effects of urea and DAP and stabilizes the ammonical nitrogen. SustainX has proven benefits of optimising F/M ratio.

1. Product Selection:
Sustainx for textile wastewater treatment

T1B SustainX—The natural replacement of UREA—DAP.

Natural powdered blend with a well-balanced 

  • C:N:P ratio, which will work in most scenarios.
  • Rich in organic carbon, bioavailable nitrogen, and phosphorus.
  • Contains natural trace elements and other nutrients essential for healthy biomass development.
  • Supports both aerobic and anaerobic microbes.

2.Dosing Schedule:

A dosing schedule was fixed for 60 days initially as follows:

DaysQuantity of T1B SustainX
Day 1 to Day 10250 kgs/day
Day 11 to Day 20200 kg/day
Day 21 to Day 30200 kg/day
Day 31 to Day 60180 kgs/day
3.The Execution:

The product was then dosed as per the efficiency of each aeration tank in series:

TanksAT-1AT-2AT-3
Capacity2500 KL1200 KL1200 KL
% of total T1B sustain quantity added60%20%20%

Results and discussions:

  • We observed a 94.5 % reduction in COD and a jump of 8% in efficiency from earlier values.
  • F/M ratio optimized to 0.234 , a rise of 64% was observed.
  • Use of MBR and the electricity to run the same was eliminated. 
  • Improved the flow rate by 12% without compromising on the outlet parameters. 

Email: sales@teamonebiotech.com

Visit: www.teamonebiotech.com

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Thermophilic vs Mesophilic Anaerobic Wastewater Treatment in Industries

The anaerobic treatment of wastewater heavily relies on trends, and unfortunately, adaptation and innovation are very slow in progression compared to rising pollution. 

Although we are all talking about the use of AIs, sensors, IOTs, and efficient hardware, unfortunately, when we consider the industrial wastewater treatment,and broader industrial effluent treatment, we are still stuck at the same processes we were 30 years ago. If you would like to know how we are optimising wastewater treatment methods in diverse environments, feel free to connect with us today.

There needs to be a continuous update at the process level, because 99 % anaerobic plants are mesophilic, i.e, work at a temperature of 30-38 *c. In regards to biocultures for wastewater treatment, the mesophilic treatment is prominent; however, the thermophilic treatment is much more effective and compatible. 

Although it is an uncommon type of ETP water treatment, when it comes to tough-to-degrade effluents such as those with recalcitrant COD, or those with phenols, Aldehydes, etc., the thermophilic microbes treatment can be a game changer in anaerobic digestion.

This blog explores when it makes sense to shift from mesophilic to thermophilic wastewater systems, the practical advantages and challenges, and what it means for plant operators and environmental engineers.

Let us start with the basics:

Parameter Mesophilic (30–38°C) Thermophilic (50–60°C)
Microbial growth rate Moderate High
Biogas yield Moderate Higher (10–25% increase)
Pathogen kill Limited Excellent (>99%)
Energy input required Lower Higher
Process stability High Sensitive to changes
Start-up time Shorter Longer

The core of the thermophilic system lies in its high-energy fast result mechanism. The hydrolysis process is much faster, resulting in increased metabolic rate and superior pathogen control in biological wastewater treatment.

Issues where thermophilic treatment can be effective:
  1. High-Strength Industrial Wastewaters:

Effluents from industries such as dairies, food processing, slaughterhouses, distilleries and starch industries have higher levels of protiens, lipids, and polysaccharides. Thermophilic systems hydrolyze and degrade these faster, leading to:

  • Higher COD, BOD degrading efficiency.
  • Higher biogas production
  • Shorter HRT (hydraulic retention time)
  • Enhanced treatment of high-strength wastewater

2. Excess Sludge and Biomass Handling Issues:

  • While most mesophilic anaerobic systems produce higher sludge, the thermophilic system produces lower quantities of excess sludge and reduces volatile solids.

3. Strict Pathogen and Odor Control: 

  • The thermophilic systems give 99% pathogen elimination in STP/Centralized ETPs that handle fecal sludge or pathogen prone waste, which is crucial if:
  • Sludge is reused in agriculture
  • Water is recycled for non-potable uses
  • Especially relevant for optimized wastewater microbiome management

4. Waste Heat:

  • In case of high waste steam, condensate, or cogeneration (CHP) units, the thermal energy can be internally sourced.
  • This supports efficient energy recovery within the plant
Microbial Diversification: Fragility Meets Efficiency

In case of the microbial cultures for wastewater treatment, the thermophilic microbes are completely different from mesophilic ones. Although thermophiles are fewer but are formidable with higher metabolic abilities in the organic waste degradation.

Key Observations:

  • Thermophilic methanogens are more sensitive to pH, VFA spikes, and loading rates.
  • Shock loads (especially of fats, solvents, or salts) can cause faster crashes.
  • Granular sludge formation is more difficult at thermophilic temperatures; biofilms or hybrid systems are better suited.
Biogas enhancement: Quantitative and Qualitative

Thermophilic systems offer 10-25 % higher biogas yield per unit COD removed. More importantly, the methane content is often higher (up to 70-75%) compared to 60-65% in mesophilic digestion.

This makes the Thermophilic process enticing where:

  • On-site biogas is used for power/steam
  • Fossil fuel replacement is a business or ESG goal
  • Carbon credit mechanisms or green energy policies apply
  • Also aligns with zero liquid discharge (ZLD) and carbon neutrality efforts
Operational & Engineering Challenges in sewage treatment process

1. Temperature maintenance:

Temperature maintenance is the key of thermophilic processes, which is altogether challenging both technically and economically, especially in large tanks and in colder environments. 

2. Narrower process Window

Thermophiles work in a smaller range.  Any variation in:

  • pH (ideal: 7.2-7.6)
  • Alkalinity ratio (IA/TA < 0.3 )
  • VFA accumulation

Can lead to performance drops

3. Start-Up Lag

Thermophilic start-up can take 30-60 days, requiring:

  • Seeding with adapted sludge
  • Step-wise temperature ramping
  • High monitoring effort

4. Foaming & Scum

Due to high gas production and surfactant sensitivity, thermophilic systems foam more easily, especially during acidification.

Know the Process, Not just the Temperature:

To be precise, a thermophilic system is not for every ETP (Eluent treatment plant), however, it is effective for any ETP where it is applied. It no doubt is high energy, difficult in operations, and with fragile microbial populations, but it always outpaces mesophilic treatment in COD/BOD control, methane gas production, and cleaner sludge.

et, it’s not a plug-and-play upgrade. You must rethink your sludge management, monitoring protocols, nutrient balancing, and energy integration.

The question isn’t whether thermophilic digestion works—it’s whether your plant is ready to manage the precision and potential that comes with it.”

If you’re designing or upgrading an anaerobic system and want to make it future-proof—especially for energy recovery or zero-liquid discharge (ZLD) ambitions—don’t ignore the thermophilic path. Just walk it carefully.

Partner with Team One Biotech for expert guidance in optimizing your ETP’s aeration and biological treatment processes. Our tailored bioculture solutions and technical expertise ensure enhanced treatment efficiency in anaerobic digestion and wastewater microbiome optimization.

Learn more at www.teamonebiotech.com or reach out at sales@teamonebiotech.com/8855050575

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Pond & Lake cleaner for successful biremediation
Successful Pilot Trial of T1BTM Pond & Lake Cleaner for Lake Bioremediation in Riaba, Malabo
  • Client: Local Authorities, Riaba, Malabo
  • Conducted By: Team One Biotech LLP
  • Trial Period: 25th April – 5th May 2025
  • Technology Used: T1B™ Pond & Lake Cleaner – Microbial Bioremediation Solution
Background

Due to nutrient pollution (high phosphate and nitrate levels), the lake in Riaba, Malabo was experiencing notable ecological damage defined by:

  1. Algal Bloom: High phosphate and nitrate levels of nutrient contamination cause too rapid algal development.
  2. Sludge Accumulation: Two feet or more of organic sludge accumulated at the bottom of the water body.
  3. Foul Odour: Strong anaerobic decomposition odour, especially during windy conditions.
  4. Ecological Imbalance: Low dissolved oxygen (DO) levels affecting aquatic health.

Team One Biotech was engaged to pilot a microbial bioremediation approach using T1B™ Pond & Lake Cleaner, recognising the need for an environmentally sustainable solution.For more information or to collaborate on similar projects, Contact Us

Action Plan – Trial before Actual 

Before initiating full-scale bioremediation of the lake, a pilot trial was strategically designed and executed to serve as a proof of concept. This small-scale trial aimed to: 

  • Validate the effectiveness of T1B™ Pond & Lake Cleaner in a controlled environment. Understand product behaviour, microbial activity, and degradation patterns when exposed to real lake water conditions, including the presence of algae and organic sludge.
  • Simulate real-world conditions (aeration, nutrient load, microbial dose) in a manageable setting using a 200-litre drum.
  • Establish dosing protocols, response timelines, and key indicators for success (e.g., reduction in BOD, ammonia, and visible algal blooms).
  • Reduce the risk of large-scale deployment by gathering actionable data and visual proof of water improvement.
  • By conducting this pilot trial, Team One Biotech ensured a data-driven, confident, and customized approach to lake restoration. The outcomes from this trial form the foundation for scaling the treatment across the full lake body, with scientifically backed expectations for ecosystem rehabilitation and lake bioremediation aiming to restore ecological balance sustainably.
Project Objectives

1. Apply Advanced Bioremediation: Using T1B Pond & Lake Cleaner. 

2. Restore Ecosystem Health: Cleanse and revive the water body. 

3. Achieve Reductions In: Algal bloom – Nutrient levels (Nitrates, Phosphates, Ammonia) – Sludge volume – Foul odours 

4. Enhance Water Quality: Improve clarity and DO. 

5. Use Natural Microbial Technology: Target breakdown of pollutants and pathogens.

Methodology

  • Setup: A 200-litre drum filled with lake water containing visible algae and organic sludge.
  • Aeration: Continuous air supply to simulate natural mixing and oxygenation.
  • Dosing: 100g/day of T1B™ Pond & Lake Cleaner.
  • Observation Period: Daily monitoring of clarity, odour, algal reduction, and biological activity.
The Solution:

  • Natural microbial strains tailored for aquatic ecosystems. 
  • Proprietary enzyme-plant extract blend.
  • Time-release formulation for sustained bioremediation.

Targets organic sludge, odours, and excess nutrients (ammonia, nitrates, phosphates).

pond & lake cleaner for bioremediation
Before vs After (10-Day Results)

ParameterBeforeAfterChange
BOD (mg/L)5.44.9-9.26%
DO (mg/L)5.24.8-7.69%
Phosphate (mg/L)1.01.0No Change
Ammonia (mg/L)0.50.3-40.00%
pH8.28.0-2.44%

Key Observations After 10 Days

  • Algal Bloom: Noticeable reduction in algal density.
  • Water Clarity: Improved water clarity
  • Odour: significantly controlled
  • Biological Activity: Aerobic biological activity initiated
Conclusion & Recommendations

The trial successfully validated the potential of T1B Pond & Lake Cleaner in restoring lake water quality through natural and sustainable microbial bioremediation. The results showed measurable reductions in pollutants and improved clarity and ecological conditions within just 10 days. 

Recommendation: Scale up the in-situ application across the lake using T1B Pond & Lake Cleaner, supported with significant aeration and regular monitoring.

Want Cleaner Water Bodies in Your Area?

Let’s make it happen — the natural way.

For collaboration, consultancy, or to implement this solution in your water bodies, please Contact Us.

???? Email: sales@teamonebiotech.com

???? Website: www.teamonebiotech.com

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