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In a multi‑stage air filtration system, medium efficiency filters (F5‑F9) handle the heaviest filtration duty. They are neither as coarse as pre‑filters (which only capture large particles) nor as expensive and restrictive as HEPA filters. Instead, they offer a balanced combination of reasonable cost and moderate pressure drop while efficiently removing fine particles such as PM2.5, bacteria, and pollen – the very pollutants that are most harmful to human health and equipment operation. This article systematically explains the efficiency classification, construction types, key parameters, typical applications, and selection & maintenance guidelines for medium filters, helping engineers and facility managers fully understand and maximize the value of this “workhorse”.

Medium efficiency filters sit between coarse (G1‑G4) and HEPA (H10‑H14) grades. According to international standards, they typically cover the following range:
| Standard System | Grade Range | Typical Efficiency Description |
|---|---|---|
| EN 779 (withdrawn) | F5‑F9 | Counting efficiency for 0.4μm particles: 40‑95% |
| ASHRAE 52.2 | MERV 9‑16 | Efficiency for 0.3‑10μm particles: 30‑95% |
| ISO 16890 | ePM2.5 40% – ePM1 >80% | Capture capability for PM2.5/PM1 |
In a typical HVAC multi‑stage filtration system, medium filters occupy the middle position:
Outdoor air → Pre‑filter (G4) → Medium filter (F5‑F9) → HEPA (optional) → Supply air
Why are they called the “workhorse”?
| Stage | Task | Load Share |
|---|---|---|
| Pre‑filter | Captures large particles (>5μm), protects downstream | About 30% of mass (mostly coarse dust) |
| Medium filter | Captures fine particles (0.3‑5μm), main purification task | About 70% of particle count load |
| HEPA | Captures sub‑micron particles for special cleanliness needs | When no HEPA is used, medium filter is the final filter |
In most commercial buildings, general hospital areas, data centers, etc., the medium filter is itself the terminal filter, directly determining the air quality delivered to the occupied space.
Although EN 779 was withdrawn in 2022, many products on the market still use this labelling; understanding it is still useful:
| Grade | Average Arrestance | Average Counting Efficiency (0.4μm) | Typical Application |
|---|---|---|---|
| F5 | — | 40‑60% | Basic medium |
| F6 | — | 60‑80% | General medium |
| F7 | — | 80‑90% | High medium |
| F8 | — | 90‑95% | Sub‑HEPA |
| F9 | — | ≥95% | Near‑HEPA |
ISO 16890 is the most authoritative standard today, using ePM1, ePM2.5, and ePM10 to directly reflect a filter’s ability to capture health‑relevant particles:
| ISO Grade | ePM1 Efficiency | ePM2.5 Efficiency | Approx. EN 779 Equivalent | Typical Application |
|---|---|---|---|---|
| ePM2.5 50% | — | ≥50% | F5‑F6 | Basic medium |
| ePM1 50% | ≥50% | ≥65% | F7 | High medium |
| ePM1 65% | ≥65% | ≥80% | F8 | Sub‑HEPA |
| ePM1 80% | ≥80% | ≥90% | F9 | Near‑HEPA |
Important note: Because of different test methods, efficiency values measured by ISO 16890 are usually lower than those labelled under EN 779. A filter claimed to be F7 may only achieve ePM1 55% under ISO 16890. Procurement should always be based on an ISO 16890 test report.
| MERV | Efficiency 0.3‑1.0μm | Efficiency 1‑3μm | Efficiency 3‑10μm | Approx. ISO Grade |
|---|---|---|---|---|
| 9 | — | — | 50‑70% | ePM10 60% |
| 10 | — | 50‑65% | — | ePM2.5 55% |
| 11 | — | 65‑80% | — | ePM2.5 70% |
| 12 | — | 80‑90% | — | ePM1 50% |
| 13 | ≥90% | ≥90% | ≥90% | ePM1 55% |
| 14 | 75‑85% | ≥90% | ≥90% | ePM1 65% |
| 15 | 85‑95% | ≥90% | ≥90% | ePM1 75% |
| 16 | ≥95% | ≥95% | ≥95% | ePM1 85% |
| Type | Principle | Advantages | Limitations | Typical Applications |
|---|---|---|---|---|
| Bag | Multiple bags in parallel, large filtration area | Very high dust‑holding capacity, long life, slow pressure‑drop rise | Bulky, not suitable for tight AHU spaces | High airflow, dusty environments; cleanroom pre‑filtration |
| Pleated (Mini‑pleat) | Media folded into compact pleats | Compact, low pressure drop, flexible installation | Lower dust‑holding capacity than bag | Data centers, commercial buildings, space‑constrained AHUs |
| Box (Mini‑pleat rigid) | Deep pleats, sturdy frame | High efficiency, robust construction | Higher cost | Pharmaceutical, hospitals, high‑cleanliness applications |
| Replaceable‑cartridge | Cartridge replaced, frame reused | Less waste, environmentally friendlier | Higher initial investment | Large central HVAC systems |
Comparison Table for Selection:
| Parameter | Bag F7 | Pleated F7 | Box F9 |
|---|---|---|---|
| Filter area (592×592) | ≈4‑6 m² | ≈2‑3 m² | ≈3‑4 m² |
| Initial pressure drop (Pa @ 2.5 m/s) | 80‑120 | 60‑100 | 100‑150 |
| Dust‑holding capacity (g @ 250 Pa) | 400‑600 | 200‑300 | 250‑400 |
| Recommended change interval (normal environment) | 12‑18 months | 9‑12 months | 12 months |
| Relative unit price (reference) | 1.0 | 0.8 | 1.3 |
Medium filter efficiency is usually expressed as counting efficiency (percentage of particles captured at a given size). For F7 and above, ePM1 efficiency (0.3‑1.0μm) is the key metric.
| Requirement | Recommended Minimum ISO Grade | Typical Efficiency |
|---|---|---|
| General PM2.5 control | ePM2.5 50% | ≥50% for PM2.5 |
| Commercial building IAQ | ePM1 50% | ≥65% for PM2.5 |
| Hospitals, data centers | ePM1 65% | ≥80% for PM2.5 |
| Cleanroom pre‑filtration | ePM1 80% | ≥90% for PM2.5 |
| Grade | Typical Initial ΔP (Pa @ rated flow) | Recommended Final Resistance (Pa) |
|---|---|---|
| F5 | 50‑70 | 150‑200 |
| F6 | 60‑80 | 180‑220 |
| F7 | 80‑120 | 200‑250 |
| F8 | 100‑150 | 250‑300 |
| F9 | 120‑180 | 300‑350 |
Impact of ΔP on energy: For a 50,000 m³/h AHU, every 50 Pa increase in pressure drop raises annual electricity cost by approximately 8,000‑12,000 RMB (at 0.8 RMB/kWh).
Dust‑holding capacity determines replacement intervals. Medium filters typically have capacities of 200‑600 g (using standard dust).
| Ambient Dust Level | Recommended Capacity | Expected Change Interval |
|---|---|---|
| Low (office) | >200 g/m² | 12‑18 months |
| Medium (mall, hospital) | >300 g/m² | 9‑12 months |
| High (factory, roadside building) | >400 g/m² | 6‑9 months |
For critical facilities such as hospitals and data centers, medium filters should meet flame‑retardant requirements:
| Standard | Class | Application |
|---|---|---|
| UL94 | HF‑1 | General commercial HVAC |
| UL94 | V‑0 | Hospitals, data centers |
| UL900 | Class 1 | Most stringent, critical facilities |
| Application | Recommended Grade | Recommended Type | Key Requirements |
|---|---|---|---|
| Commercial office | F7 (ePM1 50%) | Bag / pleated | Low noise, low ΔP |
| Shopping mall | F7 (ePM1 50%) | Bag | High dust‑holding, long life |
| General hospital ward | F7‑F8 (ePM1 50‑65%) | Bag | Flame retardant, optional antimicrobial |
| Hospital operating room (pre‑filter) | F8‑F9 (ePM1 65‑80%) | Box | Low particle shedding, silicone‑free |
| Data center | F7‑F8 (ePM1 50‑65%) | Pleated | Very low ΔP |
| Pharmaceutical cleanroom (pre‑filter) | F9 (ePM1 80%) | Bag / box | Silicone‑free, chemical‑resistant |
| School, kindergarten | F7 (ePM1 50%) | Pleated | Low noise, antimicrobial |
| Industrial plant | F5‑F7 | Bag | High dust‑holding, washable option |
| Metro, airport | F7‑F8 | Bag | High dust‑holding, flame retardant |
Start → Required indoor PM2.5 target? → ≤35 μg/m³ → F5‑F6 (ePM2.5 50%) → ≤25 μg/m³ → F7 (ePM1 50%) → ≤15 μg/m³ → F8 (ePM1 65%) → ≤10 μg/m³ → F9 (ePM1 80%) + possibly HEPA → Is installation space tight? → Yes → Pleated → No → Bag (higher dust‑holding) → Flame retardancy required? → Yes → Specify UL94 HF‑1 or V‑0 → No → Standard product → Special requirements (silicone‑free, antimicrobial, chemical‑resistant)? → Yes → Custom → No → Standard product
| Mistake | Consequence | Correct Practice |
|---|---|---|
| Choosing too high efficiency | High ΔP, high energy use, premature clogging | Select “right‑fit” efficiency based on actual cleanliness need |
| Ignoring pressure drop | Increased fan energy, higher PUE | Compare ΔP within same efficiency class; choose lowest |
| Only looking at purchase price, not lifetime | Frequent changes, high total cost | Calculate TCO; balance unit price and service life |
| Neglecting pre‑filtration | Medium filter clogs quickly | Install G4 pre‑filter upstream |
Install a differential pressure gauge and replace based on pressure drop:
| ΔP Condition | Action | Remarks |
|---|---|---|
| Initial +50% | Record, normal | — |
| 2× initial | Schedule replacement (1‑2 weeks) | Still usable, but energy already increased |
| 2.5× initial | Replace soon (within 1 week) | Energy increase significant |
| 3× initial | Replace immediately | Severe clogging, may affect airflow |
| Environment | Pre‑filter (G4) | Medium (F7) | Medium (F9) |
|---|---|---|---|
| Urban office | 6 months | 12‑18 months | — |
| Mall / hospital | 3‑6 months | 9‑12 months | 12 months |
| Data center | 6‑12 months | 12‑18 months | — |
| Factory / workshop | 1‑3 months | 6‑9 months | 9‑12 months |
For a 50,000 m³/h AHU, operating 8,760 h/year, electricity cost 0.8 RMB/kWh:
| Filter | Initial ΔP | Average Operating ΔP | Annual Electricity Cost (est.) | Saving vs. Baseline |
|---|---|---|---|---|
| Standard F7 bag | 120 Pa | 180 Pa | ≈85,000 RMB | — |
| Low‑ΔP F7 pleated | 80 Pa | 130 Pa | ≈72,000 RMB | 13,000 RMB/year |
Payback period: Low‑ΔP F7 pleated filters have about 30% higher unit cost, but the annual electricity saving recovers the difference in 6‑12 months.
Installing a G4 pre‑filter reduces the pressure‑drop rise rate of the medium filter by 40‑50%, extends its replacement interval by 30‑50%, and reduces the time the medium filter spends in high‑ΔP (high‑energy) condition.
Background: 150,000 m² floor area, 4 AHUs, originally used F5 bag filters. Indoor PM2.5 often exceeded 50 μg/m³.
Problems: Insufficient filtration efficiency led to tenant complaints; also F5 pressure drop rose quickly, requiring replacement every 4‑6 months.
Optimisation: Upgraded to F7 bag filters (ePM1 55%) and changed from fixed‑interval to ΔP‑based replacement.
Results:
Background: 5MW IT load, AHUs used F7 bag filters without pre‑filtration.
Problems: Filters replaced every 6 months; rapid pressure‑drop rise caused high fan energy consumption.
Optimisation:
Results: