Primary treatment removes 50–70% of suspended solids and 25–40% of BOD via physical processes like screening and sedimentation, while secondary treatment achieves 85–95% BOD and 90–97% TSS removal through biological oxidation. The key difference lies in pollutant type: physical solids vs biodegradable organics — with secondary systems required for discharge to sensitive environments. Misapplying treatment stages can lead to severe regulatory non-compliance, as seen in cases where industrial facilities, relying solely on primary methods for high organic loads, faced substantial penalties for exceeding discharge limits into municipal sewers or receiving waters.
What Is Primary Treatment and How Does It Work?
Primary treatment removes settleable solids and floatable materials from wastewater through physical processes, serving as the initial barrier against larger contaminants. This stage primarily relies on gravity sedimentation, allowing denser particulate matter to settle out of the water column. Typical detention times in primary clarifiers range from 1.5 to 2.5 hours, a guideline often referenced in EPA municipal wastewater treatment design standards (EPA 2024 guidelines).
Primary treatment removes 50–70% of total suspended solids (TSS) and 25–40% of biochemical oxygen demand (BOD) from the influent, as observed in general wastewater treatment practices (per Top 1 scraped content). This level of removal is a foundational step for municipal plants, but it is often insufficient for industrial wastewater streams, particularly from sectors like food processing, textile manufacturing, or pharmaceuticals, which contain high concentrations of soluble organics and fine colloids that do not readily settle.
The process flow for primary treatment typically begins with inlet works, where raw wastewater enters the plant. It then passes through mechanical bar screens, such as Zhongsheng's GX Series rotary mechanical bar screens, which remove large debris to protect downstream equipment. Following screening, grit chambers remove inert inorganic solids like sand and gravel. The wastewater then flows into primary clarifiers (sedimentation tanks), where the bulk of settleable organic and inorganic solids are removed by gravity. The settled material, known as primary sludge, is then continuously withdrawn for further processing.
How Secondary Treatment Removes Biological Contaminants
Secondary treatment employs microbial activity to biologically oxidize dissolved and colloidal organic matter, substantially reducing the organic load that primary treatment cannot address. Unlike primary treatment's physical separation, secondary processes utilize aerobic or anaerobic microorganisms to break down complex organic compounds into simpler, stable substances such as carbon dioxide, water, and new biomass.
This biological degradation achieves significantly higher removal efficiencies, typically 85–95% for BOD and 90–97% for TSS after subsequent settling (EPA Wastewater Technology Fact Sheet, 2024). These robust removal rates are crucial for meeting stringent discharge limits to sensitive receiving environments.
Common secondary treatment systems include activated sludge processes, trickling filters, oxidation ditches, and advanced membrane bioreactor (MBR) systems. In activated sludge systems, wastewater is aerated in large basins, promoting microbial growth. Hydraulic retention times (HRT) in these aeration basins typically range from 4 to 8 hours, allowing sufficient contact time for organic degradation. The 'sludge age,' which is the average time microorganisms remain in the system, varies from 5 to 15 days, depending on the organic loading and desired treatment efficacy. MBR technology, by integrating membrane filtration with biological treatment, offers a highly efficient secondary treatment method that often produces effluent suitable for reuse, outperforming conventional systems in both quality and compactness.
Performance Comparison: Primary vs Secondary Treatment Metrics

Quantitative analysis reveals distinct performance profiles between primary and secondary wastewater treatment stages across key pollutant parameters, guiding engineers in selecting the appropriate level of treatment. The fundamental difference lies in their target pollutants and removal mechanisms, which directly translate into varying effluent qualities.
For Biochemical Oxygen Demand (BOD), primary treatment typically achieves a reduction of 25–40%, primarily by removing settleable organic solids. In contrast, secondary treatment, through biological oxidation, dramatically reduces BOD by 85–95% (EPA 2024), targeting dissolved and colloidal organics. Similarly, Total Suspended Solids (TSS) removal in primary clarifiers ranges from 50–70%, while secondary treatment, especially after a secondary clarifier, consistently achieves 90–97% TSS reduction.
Chemical Oxygen Demand (COD) reduction also shows a significant divergence: primary treatment removes 30–50% of COD, whereas secondary treatment can achieve 70–90% reduction, depending on the biodegradability of the organic compounds present. Ammonia removal is negligible in primary treatment, as it is a biological process; however, nitrifying secondary systems can achieve 60–90% ammonia removal by converting it to nitrates. The physical footprint requirements differ substantially: conventional primary clarifiers may require 1.5–2 times more area than compact secondary systems like MBRs, which are known to reduce footprint by up to 60% compared to traditional activated sludge plants (per MBR case studies).
| Parameter | Primary Treatment (Typical Removal) | Secondary Treatment (Typical Removal) | Source/Notes |
|---|---|---|---|
| BOD Removal | 25–40% | 85–95% | EPA 2024, Top 1 scraped content |
| TSS Removal | 50–70% | 90–97% | EPA 2024 |
| COD Reduction | 30–50% | 70–90% | Dependent on biodegradability |
| Ammonia Removal | Negligible | 60–90% (with nitrification) | Biological process in secondary |
| Pathogen Removal | Limited | Significant (e.g., 90-99% bacteria) | Biological degradation & flocculation |
| Footprint Requirement | Larger relative to organic load | Compact for high efficiency (e.g., MBR 60% smaller) | MBR case studies |
| Pollutant Target | Settleable solids, floatables | Dissolved/colloidal organics, nutrients | Fundamental process difference |
For a deeper dive into system efficiency and return on investment, particularly for industrial applications, explore analyzing MBR system efficiency for food processing.
When to Use Primary Only vs Full Secondary Systems
The selection between primary-only and full secondary wastewater treatment systems hinges on specific influent characteristics and stringent effluent discharge standards, forming a critical decision framework for plant engineers. Relying solely on primary treatment is generally limited to scenarios where the wastewater has a low organic load or where it serves as pre-treatment before discharge into a municipal sewer system. For instance, industrial pretreatment under the EU Industrial Emissions Directive (IED 2010/75/EU) may permit primary-only treatment if the subsequent municipal plant can handle the remaining organic load and final effluent quality.
However, secondary treatment becomes necessary for direct discharge into surface waters, especially in environmentally protected zones, as mandated by regulations such as the EU Urban Waste Water Directive (91/271/EEC). This directive sets strict limits on BOD and TSS for discharges to ensure ecological health. High-strength industrial wastewater, typically characterized by a Chemical Oxygen Demand (COD) greater than 1,500 mg/L or a Biochemical Oxygen Demand (BOD) exceeding 500 mg/L, almost always necessitates an enhanced primary stage followed by full secondary treatment to meet compliance targets.
A simplified decision tree can guide this choice: if influent BOD consistently exceeds 200 mg/L, secondary treatment is almost always recommended to achieve environmental discharge standards. If influent TSS is consistently below 150 mg/L and the organic load is low, primary treatment alone might be adequate for sewer discharge. For enhancing primary treatment efficiency, particularly with high oil, grease, or colloidal solids, Dissolved Air Flotation (DAF) systems can significantly boost primary treatment efficiency, enabling better particle removal before biological stages.
Technology Overlap: How Modern Systems Blend Primary and Secondary Stages

Modern wastewater treatment technologies increasingly integrate and optimize traditional primary and secondary stages within compact, multi-functional units, blurring conventional boundaries. This evolution is driven by the need for smaller footprints, higher efficiency, and consistent effluent quality, particularly in industrial settings where space and performance are critical.
Integrated systems, such as Zhongsheng's WSZ series underground integrated sewage treatment plants, exemplify this trend. These compact units combine anoxic and aerobic biological zones with internal settling or membrane filtration, effectively performing both secondary and often tertiary treatment within a single reactor. This design eliminates the need for separate primary clarifiers in many applications, especially for domestic or low-to-medium strength industrial wastewater, offering a complete treatment solution that is often installed underground to save valuable surface area.
Technologies like Dissolved Air Flotation (DAF), traditionally considered an enhanced primary treatment, can remove colloidal and oily matter with high efficiency, often achieving better TSS and FOG (Fats, Oils, and Grease) reduction than conventional primary clarifiers, thus significantly improving the influent quality for subsequent biological stages. Membrane Bioreactor (MBR) systems represent another significant overlap; they combine the biological degradation of secondary treatment with membrane filtration, effectively eliminating the need for a secondary clarifier and producing an effluent quality that often surpasses conventional secondary treatment standards, approaching tertiary levels. Modular units integrating these technologies can reduce the overall plant footprint by 40–60% compared to conventional multi-stage train setups, offering flexible and scalable solutions for diverse industrial and municipal needs.
Frequently Asked Questions
Common inquiries regarding primary and secondary wastewater treatment often focus on functional differences, application scenarios, and comparative system performance.
What is the main difference between primary and secondary treatment?
Primary treatment physically removes large settleable solids and floatables through screening and sedimentation. Secondary treatment biologically degrades dissolved and colloidal organic matter using microorganisms in an aerobic or anaerobic environment.
Can primary treatment be used alone?
Yes, primary treatment can be used alone for pre-treatment before discharge to a municipal sewer system, especially if the wastewater has a low organic load. However, it is generally insufficient for direct discharge into natural receiving environments due to inadequate organic and pathogen removal.
Which is better: SBR or MBBR for secondary treatment?
Both Sequential Batch Reactors (SBR) and Moving Bed Biofilm Reactors (MBBR) are effective biological secondary treatment methods, but they excel in different areas. SBRs offer excellent nutrient removal capabilities due to their batch operation flexibility, making them suitable for fluctuating flows. MBBRs, with their biofilm carriers, provide a smaller footprint, higher volumetric loading, and greater resilience to shock loads, making them ideal for space-constrained industrial applications. For a more detailed comparison, you can explore the nuances of aerobic vs. anaerobic processes and their system types.
What is primary vs secondary sludge?
Primary sludge consists of the raw, settleable solids and floatable materials removed during primary sedimentation. It typically has a higher organic content and is more putrescible. Secondary sludge, also known as biological sludge or activated sludge, is composed primarily of the excess biomass (microorganisms) generated during the biological treatment process in the secondary stage. It typically has a lower solids concentration but contains a higher proportion of living and dead microbial cells.
Does secondary treatment remove microplastics?
Secondary treatment can partially remove microplastics, with removal efficiencies often reported up to 80% or more, largely dependent on the effectiveness of the secondary clarifier and the ability of microplastics to adhere to biological flocs. However, it does not reliably remove all microplastics, especially smaller particles, without additional advanced filtration or tertiary treatment stages. To understand the distinction between secondary and tertiary treatment, refer to our article on