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Single-Use Systems Explained | Cell Culture Technology

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TECHNOLOGY EXPLAINER

Single-Use Systems
— when the wall of the culture vessel changed from stainless steel to multilayer film

Single-use manufacturing means using culture bags, tubing, connectors and filters once and then discarding them. It removes the need for cleaning and cleaning validation, but in exchange the surface that touches the drug is now a polymer. In 2013 it was reported that a breakdown product of an antioxidant in that polymer inhibits cell growth. For materials engineers, this is the part of cell culture with the most points of contact.

Built from primary sources: film makers' technical documents (specifications of their own products), peer-reviewed papers, and published material from ICH, USP, the US Code of Federal Regulations and BioPhorum / Last updated September 2026

Conceptual image of a plain, translucent roll of polymer film on a dark surface, with a short length of film drawn out from it
AI-generated concept image. An impression of the theme “a polymer film that becomes the wall of a drug-manufacturing vessel”. It does not represent any real product, or the colour, layer structure or thickness of any film.
What this article covers
  1. What a single-use system is, in three points
  2. The multilayer film of a culture bag: contact layer, gas barrier, outer layer
  3. Gamma sterilisation and antioxidants: the breakdown product that held back cell growth
  4. A materials engineer's view (1): antioxidants are necessary, but their breakdown products are the problem
  5. Extractables and leachables (E&L) and how they are assessed: ICH Q3E, USP <665> and <1665>, BioPhorum
  6. Our calculation: the smaller the vessel, the more polymer per millilitre
  7. Compared with stainless steel: cleaning, validation, waste
  8. The upper limit on volume: 2,000 L and 5,000 L
  9. A materials engineer's view (2): the supplier now owns part of the drug manufacturing process
  10. What could not be confirmed, and open problems
  11. Glossary / References / Claim-to-source audit
How claims are labelled in this article

Sourced = stated in published material or a peer-reviewed paper (link given)
Our calculation = a value this article derived from assumptions it states
Not yet confirmed = a draft, plan or outlook that is not settled
Structural readings and materials-design interpretations are marked separately as Commentary. Companies' technical documents are used only for facts about that company's own products.

1. What a single-use system is, in three points

A single-use system is an approach in which the wetted parts of culture vessels and piping are pre-sterilised polymer components that are replaced after every use. A stainless-steel tank is cleaned, steam-sterilised and reused; in single-use manufacturing the whole bag is swapped out.

  • The benefit: a 1999 paper on a wave-type bioreactor notes that because it is disposable, it needs no cleaning or sterilisationSourced. Researchers at an equipment maker list a lower risk of cross-contamination and shorter lead times among the advantagesSourced
  • How large: a film maker's documents show bags from 50 mL to 2,000 L made from the same film. Another equipment maker sells a 5,000 L single-use bioreactorSourced
  • The new problem: because the surface touching the drug is now a polymer, chemical species that leach out of the polymer (leachables) have to be assessed. In 2013 researchers at Amgen reported that a breakdown product derived from an antioxidant in polyethylene strongly inhibits cell growthSourced
The single most important line in this article

A bag maker itself states in its technical literature that as single-use systems replace traditional stainless-steel equipment, suppliers take on a more critical part of the drug manufacturing processSourced. The choice of film resin and additives has become part of the quality of the drug itself (our commentary).

2. The multilayer film of a culture bag: contact layer, gas barrier, outer layer

The wall of a culture bag is not a single polymer but a coextruded multilayer film. Here are two films whose layer structures the makers have published.

Layer structure of culture-bag films (drawn from the makers' published documents) The top is the outside; the bottom is the surface in contact with the culture (the contact face). Aegis5-14 (Thermo Fisher) S80 (Sartorius) Outer: polyester elastomer 0.8 Tie layer 0.9 Gas barrier: EVOH 1.0 Tie layer 0.9 Contact layer: polyethylene 10.4 (about 74% of the thickness) Outer: LLDPE Core: EVOH Contact layer: LLDPE ▲ Contact face (culture side) ▲ Contact face (culture side) Note: left: layer order and values from Thermo Fisher's schematic [Ref. 1] (sum 14.0 = the 14 mil gauge); heights drawn to scale. Note: right: layer order and 400 µm total from Sartorius [Ref. 2]. Layer ratios are not given, so the layers are drawn equal.
Fig. 1 Concept diagram (vector drawing). Layer names and order follow each maker's technical documents [Refs. 1 and 2]. The layer heights on the left are proportional to the values in the schematic in the document (0.8 / 0.9 / 1.0 / 0.9 / 10.4, total 14.0), and “about 74%” is this article's calculation (10.4 / 14.0). The layer thickness ratios on the right have not been published, so they are drawn equal and are not the real proportions.
ItemAegis5-14 (Thermo Fisher)S80 (Sartorius)
StructureFive-layer, 14 mil cast film. Coextruded outer layer of polyester elastomer / EVOH barrier layer / low-density polyethylene contact layerCoextruded PE | EVOH | PE structure. Contact layer LLDPE; backbone LLDPE and EVOH
Thickness0.356 mm (0.014 in.)400 µm
Oxygen transmission rate0.36 cc/m²/day (23 °C, 90% RH inside)“High gas and water-vapour barrier” (no figure in the documents consulted for this article)
Water-vapour transmission rate0.35 g/m²/day (23 °C)As above
Operating temperature range−80 °C to 60 °CNot stated in the documents consulted for this article
SterilisationGamma irradiation at 25 to 40 kGy for a sterility assurance level of 10⁻⁶ (stated to comply with ANSI/AAMI/ISO 11137:2006). Physical properties measured after irradiationRadiation sterilisation under ISO 11137, with gamma dose mapping stated to be carried out
Role of the contact layer (as stated by the maker)Contact material: polyethyleneFilm strength and flexibility, weld strength, low extractables, excellent biocompatibility

All Sourced (Thermo Fisher Aegis5-14 document [Ref. 1], Sartorius Flexsafe document [Ref. 2]). These are each company's statements about its own products and are not representative of other companies' products or the industry as a whole.

Our calculation: layer thickness, and what the barrier layer is protecting
  • Layer thickness: with 1 mil = 25.4 µm, the Aegis5-14 contact layer is 10.4 × 25.4 ≈ 264 µm and the EVOH layer 1.0 × 25.4 ≈ 25 µm. The whole film, 14 mil ≈ 356 µm, matches the 0.356 mm in the documentOur calculation
  • Oxygen passing through: converting 0.36 cc/m²/day as a gas at standard conditions (22.4 L/mol), about 0.016 mmol of oxygen passes through 1 m² per day
  • Comparison: as calculated in our bioreactor explainer, CHO cells at 20 million cells/mL use about 4.58 mmol of oxygen per litre of culture per hour. 0.016 / 4.58 = 0.0035 h, or about 13 seconds' worth

Reading: the oxygen that passes through the film is orders of magnitude smaller than what cells in culture consume. What the EVOH gas barrier protects, it seems, is not the oxygen supply during culture but the quality of media, buffers and drug substance during long storage. Sartorius also describes S80's high gas and water-vapour barrier as suited to the long-term storage of media, buffers and drug substanceSourced (our commentary). Assumptions and limits: the transmission rate is a 23 °C value and will differ at the culture temperature of 37 °C. The 22.4 L/mol conversion is also an approximation.

3. Gamma sterilisation and antioxidants: the breakdown product that held back cell growth

Single-use bags arrive already sterilised by gamma irradiationSourced. This is where the question of polymer additives comes in. In 2013 researchers at Amgen (Hammond and colleagues) reported the following in the PDA JournalSourced.

  • What was found: of the many chemical species extracted at low levels from bag materials, bis(2,4-di-tert-butylphenyl) phosphate (bDtBPP) was strongly detrimental to cell growth
  • Where it came from: it is a breakdown product of tris(2,4-di-tert-butylphenyl) phosphite (trade name Irgafos 168), a common antioxidant in many formulations of polyethylene, the polymer often used for contact layers
  • At what level: detrimental effects appeared in several mammalian cell lines at concentrations well below the ppm level
  • Under what conditions: migration from the film depended on time and temperature. Exposure of oxidised Irgafos 168 to ionising radiation such as gamma rays was suggested as an important condition for producing large amounts of bDtBPP
From antioxidant to a breakdown product harmful to cells (our framing) A flow based on the report by Hammond et al. (2013) and a film maker's documents. Antioxidant added Phosphite type (Irgafos 168) Common in polyethylene Extrude, irradiate Shields the polymer from oxidation: its job Breakdown: bDtBPP Suggested to form in bulk when the oxidised additive is irradiated Leaches into medium Depends on time, temp. Inhibits cell growth Harmful well below the ppm level Resin and film side (maker's statements) Limit phosphite antioxidant or omit it from the contact layer Control resin specs, extrusion and irradiation conditions Testing side (maker's statements) Extract with water or ethanol and measure bDtBPP Run cell-growth tests on irradiated bags Note: the top row follows Hammond et al. [Ref. 5]; the bottom row follows Sartorius documents [Refs. 2 and 4]. Note: the five steps are our framing and show neither the reaction mechanism nor any quantitative link between steps. Note: the bottom row describes one company's own products and is not presented as common industry practice.
Fig. 2 Concept diagram (vector drawing). Each step in the top row follows the abstract of Hammond et al. [Ref. 5], and the measures in the bottom row follow Sartorius documents [Refs. 2 and 4]. Organising this into five steps and two sets of measures is this article's own and does not show the chemical mechanism or quantitative relationships.

4. A materials engineer's view (1): antioxidants are necessary, but their breakdown products are the problem

Why this matters for materials engineers: the gap between reducing an additive and removing it

Sartorius's 2020 white paper cites the report by Hammond and colleagues and then makes the following point.

Antioxidants are needed to keep the film stable, protecting the polymer from oxidation during extrusion and gamma irradiation. To ensure proper cell growth, it is critical to optimise the concentration of these additives and control it tightlySourced.

The company says that in its S80 film the concentration of phosphite antioxidant is limited, and that in a separate ethylene vinyl acetate film (S71) this antioxidant is not included in the contact layerSourced. It also shows in a figure that, if the additive formulation is not controlled, the age of a bag (its storage time after irradiation) can affect cell growthSourced.

The lesson is that gamma sterilisation is not just a step before use; it is a step that changes the chemistry of the material.

  • Cut the antioxidant too far, and the polymer itself degrades during extrusion and irradiation
  • Add too much, and irradiation produces more breakdown products that harm the cells
  • And the amount of breakdown product changes with extrusion conditions, irradiation conditions and storage time

In another document the company also writes that transparency does not mean purity: there is no correlation between a film's clarity and its extractables and leachables profileSourced. A film that looks clean is not necessarily clean from the cells' point of view. Only suppliers able to manage additive formulation, extrusion, irradiation and storage as one system can meet the basic conditions of this market: that is how this reads (our commentary).

5. Extractables and leachables (E&L) and how they are assessed: ICH Q3E, USP <665> and <1665>, BioPhorum

(1) Definitions: the ICH Q3E draft

The draft of Q3E, the extractables and leachables guideline of the International Council for Harmonisation of Technical Requirements for Pharmaceuticals for Human Use (ICH), defines the two terms as followsSourced.

  • Leachables: chemical entities that migrate into the drug product from manufacturing components and systems, packaging, or delivery device components under the defined manufacturing conditions and labelled storage conditions
  • Extractables: chemical entities deliberately extracted from the same components under defined laboratory test conditions, and therefore potential leachables
Extractables and leachables, and three stages of risk assessment (from the ICH Q3E draft) Left = how the terms relate / right = the risk-assessment procedure set out in the draft Extractables Chemicals deliberately drawn out under lab conditions Harsh solvents, heat and time to see the worst case = candidates for leachables Leachables Chemicals that migrate into the drug under real manufacturing and storage These are what reach the patient Stage 1: hazard identification Find leachables that may migrate from contact surfaces Stage 2: risk analysis Quantify leachables and assess patient exposure Stage 3: integrated risk evaluation Judge acceptability from impact on quality, safety, efficacy Example measures Change parts or suppliers, pre-wash, pre-flush, add purification Note: definitions, stages and measures follow the ICH Q3E draft (Step 2, published 1 August 2025 for comment) [Ref. 8]. Note: the nested boxes on the left are our framing: some extractables become leachables. They do not show quantities. Note: the draft is not final. The final version (Step 4) is scheduled for June 2027 [Ref. 9].
Fig. 3 Concept diagram (vector drawing). The definitions, three stages and example measures follow the ICH Q3E draft [Ref. 8], and the planned timing of finalisation follows the guideline's work plan [Ref. 9]. Showing them as nested boxes is this article's framing and does not represent the ratio of extractables to leachables. The draft may change.

(2) What the ICH Q3E draft says about manufacturing components

For components and systems used in drug manufacturing (including polymeric manufacturing equipment components), the draft says the followingSourced.

  • Its scope includes cell and gene therapy products
  • Extraction studies on manufacturing components should be designed to represent the worst case of the manufacturing conditions (for example, the smallest scale with the longest contact time, and the highest temperature and pressure)
  • The leachables risk from manufacturing components is recognised as lower than that from packaging, because contact times are relatively short and the volume of liquid relative to surface area is large
  • Leachables introduced upstream may be removed in downstream steps
  • Where several components of the same or similar materials are used, the leachables risk should be assessed cumulatively
  • If all extractable peaks are at or below the analytical evaluation threshold (AET) and there are no Class 1 leachables, the risk may be considered minimal and acceptable

(3) USP <665> and <1665>

The United States Pharmacopeia (USP) has two chapters on plastic components and systems used in drug manufacturingSourced.

ChapterTitle (as on the USP official page)Status as confirmed for this article
<665>Plastic Components and Systems Used to Manufacture Pharmaceutical Drug Products and Biopharmaceutical Drug Substances and ProductsThe USP page states that it is an informational chapter and does not apply as a compendial requirement unless specified by a regulatory or enforcement authority
<1665>Characterization and Qualification of Plastic Components and Systems Used to Manufacture Pharmaceutical Drug Products and Biopharmaceutical Drug Substances and ProductsA chapter on the characterisation and qualification of plastic components and systems (full text available to subscribers)

All Sourced (the official USP page for each chapter [Refs. 6 and 7]). The full text of each chapter (details of test methods, solvents and conditions) is for subscribers and was not checked for this article. The official dates are also not stated, because the USP notice page could not be accessed and they could not be confirmed in primary sources.

(4) The BioPhorum extractables testing protocol

BioPhorum (formerly BPOG), an industry group of drug makers and suppliers of single-use components, updated its extractables testing protocol on 22 April 2020. According to the group's page, the main changes from the 2014 version were as followsSourced.

  • 5 M sodium chloride and 1% polysorbate 80 were dropped from the extraction solvents (because their inherent extraction power was low)
  • Time-zero sampling was dropped (because compounds detected then were detected at higher levels at later time points)
  • Elemental analysis of the 50% ethanol extract was dropped
  • The overall testing burden was cut by 30 to 50%, and an “extractables ecosystem” framework for sharing extractables data across the supply chain was introduced

Underlying all of this is a US federal regulation, 21 CFR 211.65, which requires that “surfaces that contact components, in-process materials, or drug products shall not be reactive, additive, or absorptive so as to alter the safety, identity, strength, quality, or purity of the drug product beyond the official or other established requirements”Sourced. The requirement is the same for stainless steel and for polymer (our commentary).

6. Our calculation: the smaller the vessel, the more polymer per millilitre

The ICH Q3E draft names “the smallest scale” as a worst case, and gives “the large volume of liquid relative to surface area” as a reason why manufacturing components carry lower riskSourced. Both follow from the fact that the larger the vessel, the less polymer area there is per millilitre of liquid. Here is the calculation for a cubic vessel.

Our calculation: wetted area per millilitre of liquid
  • Assumption: treat the vessel as a completely filled cube with all six faces wetted (real bags are not cubes)
  • Formula: a cube of side L cm has an area of 6L² cm² and a volume of L³ mL, so area / volume = 6 / L (cm²/mL)
  • 1 L (side 10 cm): 6 / 10 = 0.60 cm²/mL
  • 100 L (side 46.4 cm): 6 / 46.4 = 0.13 cm²/mL
  • 2,000 L (side 126 cm): 6 / 126 = 0.048 cm²/mL

Per millilitre of liquid, a 1 L vessel touches about 12.6 times as much polymer as a 2,000 L vesselOur calculation. A 1,000-fold increase in volume cuts area / volume to a tenth (one over the cube root of 1,000). Assumptions and limits: flat bags (2D bags) have a larger area / volume than a cube. The area of tubing, connectors and filters is not included.

Vessel size and wetted area per mL of liquid (our calculation) Assumes a completely filled cube. The vertical axis is in cm²/mL. 0 0.2 0.4 0.6 0.60 0.28 0.13 0.060 0.048 1 L 10 L 100 L 1,000 L 2,000 L ← about 12.6x the 2,000 L value Note: all values were calculated by this article and are not measurements. Real bag shapes and tubing/filter areas are excluded. Note: the idea that the smallest scale is the worst case follows the ICH Q3E draft [Ref. 8].
Fig. 4 Drawing based on our calculation (vector drawing). The bar values and “about 12.6 times” were calculated by this article on the assumption of a completely filled cube and are not published figures. The ideas that the smallest scale is the worst case and that a large volume relative to surface area lowers leachables risk follow the ICH Q3E draft [Ref. 8].

7. Compared with stainless steel: cleaning, validation, waste

AspectStainless steel (reused)Single-use (disposable)
Cleaning and sterilisationClean-in-place (CIP) and steam-in-place (SIP) are required. US federal regulations require written procedures for cleaning and maintenance (responsibility, schedules, methods, removal of previous batch identification and so on) [Ref. 12]“Disposable, so no cleaning or sterilisation is needed” [Ref. 17]. Supplied gamma-sterilised [Ref. 1]
Water and energyWater use is mainly associated with CIP and SIP and is a major environmental burden. Producing purified water and water for injection, and cleaning and sterilisation, are energy-intensive [Ref. 13](Water and energy use are expected to fall because CIP and SIP are no longer needed) [Ref. 13]
Speed of deploymentFixed equipment is costly, and installing and qualifying tanks and their utilities takes long lead times [Ref. 14]Shorter lead times and lower cross-contamination risk [Ref. 15]. Design changes can be implemented faster [Ref. 14]
Accumulated design knowledgeBecause its geometry is well known and defined, it is described as “still the gold standard” [Ref. 15]Shapes, agitation principles and aeration methods differ between products, which can make process transfer and scale-up a challenge [Ref. 15]
Assessment of the materialThe wetted surface is metal. The requirement of 21 CFR 211.65 is the same [Ref. 11]Extractables and leachables from the polymer must be assessed (Section 5)
WasteThe equipment is used again and againUsed bags, tubing and filters become solid waste (our commentary)

Items with a source are Sourced. However, “water and energy use fall” is an expectation stated in the conclusion of Bunnak and colleagues (2016), who compared fed-batch and perfusion processesNot yet confirmed; that paper itself covers stainless-steel facilities and leaves the manufacture of consumables outside its scope [Ref. 13].

In the life-cycle assessment by Bunnak and colleagues, CIP and SIP accounted for more than 85% of total water use in a perfusion process under one set of conditionsSourced. The Amgen researchers also write, in the lay summary of their paper, that replacing stainless-steel tanks with disposable bags brings significant environmental and cost advantagesSourced. On the other hand, a comparison that includes the manufacture and disposal of the single-use components themselves could not be found in the primary sources consulted for this article.

8. The upper limit on volume: 2,000 L and 5,000 L

Published volume ranges (log scale) Each tick is a factor of 10. The top three are ranges each company has published for its own products. Bags made from a single film 50 mL to 2,000 L (Aegis5-14) Single-use stirred-tank family 50 to 2,000 L (Dreher et al.) Single-use bioreactor 5 to 5,000 L (DynaDrive) Large-scale stainless-steel tanks 1,000 to over 25,000 L (Li et al.) 10 mL 100 mL 1 L 10 L 100 L 1,000 L 10,000 L 100,000 L Note: sources: Aegis5-14 [Ref. 1], Dreher et al. [Ref. 15], DynaDrive [Ref. 16], stainless-steel tanks [Ref. 14]. Note: the top three are product ranges, not limits for single-use overall. The steel bar is cut off as its top is open-ended. Note: the arrangement is this article's framing.
Fig. 5 Concept diagram (vector drawing). Each range follows Refs. 1, 14, 15 and 16. The top three are the product ranges of specific companies and do not show the upper limit of single-use technology as a whole or the state of the market. The bar positions were drawn by this article on a log scale.

Thermo Fisher describes its single-use bioreactor as available from 5 L to 5,000 L and as the first 5,000 L single-use bioreactor on the market, and says Aegis5-14 film can be used for its bagsSourced. Stainless-steel tanks, meanwhile, have dominated large-scale manufacturing at 1,000 to more than 25,000 LSourced.

What sets the upper limit? The primary sources offer two clues.

  • The weight of the liquid: Sartorius says bags for large-scale mixing and stirred tanks must withstand the high hydrostatic pressure generated by 2,000 to 3,000 L of liquidSourced
  • How hard it can be stirred: in large single-use tanks, physical constraints are said to limit the maximum P/V to around 20 to 30 W/m³Sourced
Our calculation: the pressure at the bottom of a 2,000 L bag

Assumptions: a cylinder with height / diameter = 2 (the ratio of Dreher and colleagues' stirred tanks) and a liquid density of 1,000 kg/m³.
From volume V = (π/4)D² × 2D = (π/2)D³ = 2 m³, D ≈ 1.08 m and liquid depth H ≈ 2.17 m.
Hydrostatic pressure at the bottom = 1,000 × 9.81 × 2.17 ≈ 21 kPa (about 0.21 atm)Our calculation.

The pressure itself is not large, but it means that a film 0.36 to 0.4 mm thick is holding two tonnes of liquid while being pressed against a rigid outer container. That Sartorius lists, for large 3D bags, a point-of-use test that detects large leaks (100 to 200 µm) after installation in the appropriate containerSourced can be read as reflecting that some things can only be checked in that state (our commentary). Assumptions and limits: the shape and liquid depth of real tanks differ by product, and the stress on the film is set by how it bears against the outer container.

9. A materials engineer's view (2): the supplier now owns part of the drug manufacturing process

Conceptual image of several thin translucent sheets in slightly different tints, stacked with small offsets on a dark surface
Fig. 6 AI-generated concept image. An impression of the idea of stacking polymer layers with different roles into a single film. It does not show the real number, thickness or colour of the layers, or the structure of a coextrusion.
Why this matters for materials engineers: speaking the language of assessment is the price of entry

With stainless-steel equipment, a drug maker only had to specify the material (steel grade, surface finish) and validate the cleaning. With single-use, resin, additives, extrusion, welding, irradiation and storage all sit inside the supplier's process. Sartorius's document says it designs, manufactures, quality-controls and sterilises its bags under conditions that mirror drug manufacturing, meeting requirements close to cGMPSourced.

On top of that, the “language” of assessment is taking shape.

  • The ICH Q3E draft: definitions of extractables and leachables, the worst-case approach, cumulative risk assessmentSourced
  • USP <665> and <1665>: chapters on plastic components used in manufacturing (with <665> stated to be informational)Sourced
  • The 2020 BioPhorum protocol: standard extraction testing with fewer solvents and time points, and a framework for sharing dataSourced

For materials makers, there are two implications (our commentary).

  • Disclosing and controlling additives in a resin grade becomes a source of value. A resin whose antioxidant type and amount, and the behaviour of its breakdown products (particularly after gamma irradiation), can be explained is easier for film makers to build assessment data on
  • Standardised data can be reused for the next customer. As BioPhorum's “extractables ecosystem” for sharing data across the supply chain makes clearSourced, data gathered once under the protocol gets reused. Conversely, changing the resin or additive means rebuilding that body of data

It is the same pattern as the “development standard material” discussed in our explainer on argyrodite solid electrolytes. A material that has become the basis of a body of assessment data is not easily displaced, even by a competitor with equal performance (our commentary).

Why this matters for materials engineers: quality expressed as the size of a pinhole

Sartorius says that for 2D bags and 3D bags up to 500 L, pre-shipment integrity testing guarantees no defects larger than 2 µm, and gives detection limits for point-of-use testing of 10 µm for 2D bags and 100 to 200 µm for large leaks in large 3D bags after installationSourced.

The larger the volume, the coarser the defects that can be detected on site. This means that not creating defects in the film and welds in the first place matters more than inspection (our commentary). A multilayer film about 0.4 mm thick holds two tonnes of liquid while keeping it sterile. The uniformity of the material and the process capability of the welding become, in effect, the product's sterility assurance.

10. What could not be confirmed, and open problems

(1) The full text and official dates of USP <665> and <1665>

The chapter texts are for subscribers, and details such as test solvents and conditions were not checked for this article. The official dates are also not stated, because the USP notice page could not be accessed and they could not be confirmed in primary sources.

(2) ICH Q3E is still a draft

It is a draft published at Step 2 on 1 August 2025, and the work plan expects the final version (Step 4) in June 2027Not yet confirmed. The content may change before it is finalised.

(3) Layer structures of other companies' films

This article covers only the two products whose layer structures and thicknesses the makers show in published documents. Resin names and layer structures of other companies' products are not stated beyond what could be confirmed in primary sources.

(4) An overall comparison of environmental impact

Within the scope of this article, no primary source could be found comparing single-use and stainless steel with the manufacture and disposal of single-use components included.

The article in summary
  • The wall of a culture bag is a multilayer film. In the published examples the contact layer is polyethylene, with an EVOH gas barrier at the coreSourced
  • What the gas barrier protects is quality during storage. The oxygen passing through the film was orders of magnitude less than what cells consumeOur calculation
  • A breakdown product of an antioxidant in polyethylene (bDtBPP) inhibits cell growth, as reported in 2013, with gamma irradiation suggested as an important conditionSourced
  • The assessment framework is taking shape in the ICH Q3E draft, USP <665> and <1665>, and the BioPhorum protocol. Q3E is still a draftNot yet confirmed
  • The smaller the vessel, the more polymer area per millilitre of liquid: 1 L is about 12.6 times 2,000 LOur calculation
  • Single-use products have been published up to 2,000 L, and at most 5,000 L, while stainless steel reaches beyond 25,000 LSourced

11. Glossary

Single-use system
A manufacturing approach in which wetted parts are pre-sterilised polymer components replaced after each use.
Coextruded film
A single multilayer film made by extruding several polymers at the same time.
Contact layer
The layer of a film in direct contact with the culture or drug. Polyethylene in the published examples.
EVOH
Ethylene vinyl alcohol copolymer. Used as a gas-barrier layer that lets little oxygen through.
LLDPE
Linear low-density polyethylene. Flexible and easy to weld.
Gamma sterilisation
Sterilisation that kills microorganisms with radiation, to the ISO 11137 standard. It can also change the chemistry of polymers and additives.
Sterility assurance level (SAL)
The probability that a single microorganism survives sterilisation. 10⁻⁶ means one in a million.
Extractables
Chemical entities deliberately extracted from components under laboratory conditions. Potential leachables.
Leachables
Chemical entities that migrate into the drug under real manufacturing and storage conditions.
bDtBPP
A breakdown product of the antioxidant Irgafos 168, reported to inhibit cell growth.
AET
Analytical evaluation threshold. A guide above which extractables are identified and assessed.
CIP / SIP
Clean-in-place / steam-in-place. Cleaning and sterilising stainless-steel equipment without taking it apart.
BioPhorum (formerly BPOG)
An industry group of drug makers and suppliers. Publishes a standard protocol for extractables testing.
Integrity testing
Testing that confirms a bag has no leaks (pinholes and the like).

12. References (primary sources)

  1. Thermo Fisher Scientific “Thermo Scientific Aegis5-14 film — Five-layer, 14 mil cast film”, product document (COL01764, 2019) — documents.thermofisher.com
  2. Sartorius “Flexsafe 2D & 3D Pre-Designed Solutions for Storage and Shipping”, product document — sartorius.com
  3. Sartorius “Flexsafe New PE Film. New Benchmark.”, product document (SPT1503) — api.sartorius.com
  4. Sartorius (Lugari A, Schenk T) “Cell Growth Performance in Single-use Bags”, white paper (15 April 2020) — sartorius.com
  5. Hammond M et al. (Amgen) “Identification of a leachable compound detrimental to cell growth in single-use bioprocess containers”, PDA J Pharm Sci Technol 67(2):123–134 (2013) (PubMed abstract) — pubmed.ncbi.nlm.nih.gov
  6. United States Pharmacopeia (USP) “<665> Plastic Components and Systems Used to Manufacture Pharmaceutical Drug Products and Biopharmaceutical Drug Substances and Products”, official page — doi.usp.org
  7. United States Pharmacopeia (USP) “<1665> Characterization and Qualification of Plastic Components and Systems Used to Manufacture Pharmaceutical Drug Products and Biopharmaceutical Drug Substances and Products”, official page — doi.usp.org
  8. ICH “Guideline for Extractables and Leachables Q3E”, draft (Step 2, 1 August 2025) — database.ich.org
  9. ICH “ICH Q3E EWG Work Plan” (8 February 2025) — database.ich.org
  10. BioPhorum “Disposables: Extractables testing of polymeric single-use components used in biopharmaceutical manufacturing” (22 April 2020) — biophorum.com
  11. US Code of Federal Regulations “21 CFR 211.65 Equipment construction” — ecfr.gov
  12. US Code of Federal Regulations “21 CFR 211.67 Equipment cleaning and maintenance” — ecfr.gov
  13. Bunnak P et al. (University College London and others) “Life-cycle and cost of goods assessment of fed-batch and perfusion-based manufacturing processes for mAbs”, Biotechnology Progress 32(5):1324–1335 (2016) — pmc.ncbi.nlm.nih.gov
  14. Li F et al. (Genentech) “Cell culture processes for monoclonal antibody production”, mAbs 2(5):466–479 (2010) — pmc.ncbi.nlm.nih.gov
  15. Dreher T et al. (Sartorius Stedim Biotech) “Design space definition for a stirred single-use bioreactor family from 50 to 2000 L scale”, BMC Proceedings 7(Suppl 6):P55 (2013) — pmc.ncbi.nlm.nih.gov
  16. Thermo Fisher Scientific “DynaDrive Single-Use Bioreactor”, product page — thermofisher.com
  17. Singh V “Disposable bioreactor for cell culture using wave-induced agitation”, Cytotechnology 30:149–158 (1999) — pmc.ncbi.nlm.nih.gov
  18. Lemire L et al. “Scale-up of a monoclonal antibody CHO fed-batch production in stirred tank bioreactors: Effect of hydrodynamic conditions and feeding regimen”, Biotechnology Progress (January–February 2026 issue, doi:10.1002/btpr.70073) — pmc.ncbi.nlm.nih.gov

13. Claim-to-source audit

Claim in the textBasisLabel
That Aegis5-14 is a five-layer, 14 mil cast film coextruded from a polyester elastomer outer layer, an EVOH barrier layer and a low-density polyethylene contact layer. The layer order in the schematic (polyester / tie / EVOH / tie / polyethylene) and values (0.8 / 0.9 / 1.0 / 0.9 / 10.4). Thickness 0.356 mm, oxygen transmission 0.36 cc/m²/day, CO2 transmission 1.35 cc/m²/day, water-vapour transmission 0.35 g/m²/day, −80 °C to 60 °C, gamma irradiation at 25 to 40 kGy for SAL 10⁻⁶ (ANSI/AAMI/ISO 11137:2006), polyethylene as the contact material, BPCs from 50 mL to 2,000 L, and supply in gamma-irradiated formThermo Fisher Aegis5-14 document. Reference 1 https://documents.thermofisher.com/TFS-Assets/BPD/Datasheets/aegis5-14-film-fact-sheet.pdfSourced
That S80 is a 400 µm coextruded PE | EVOH | PE structure (contact layer LLDPE; backbone LLDPE and EVOH). The role of the contact layer (strength, flexibility, weld strength, low extractables, biocompatibility). That the high gas and water-vapour barrier suits long-term storage of media, buffers and drug substance. ISO 11137 and dose mapping. Minimising antioxidants. That the company makes its bags under conditions that mirror drug manufacturing, and states that suppliers take on a more critical part of the drug manufacturing process. No defects above 2 µm in pre-shipment integrity testing (2D, and 3D up to 500 L); point-of-use detection limits of 10 µm (2D) and 100 to 200 µm for large 3D bags after installationSartorius Flexsafe 2D & 3D document. Reference 2 https://www.sartorius.com/download/340044/broch-flexsafe-2d-3d-bags-sp-1518-e-data.pdfSourced
That transparency does not mean purity (no correlation between film clarity and extractables and leachables profile). That bags for large-scale mixing and stirred tanks must withstand the hydrostatic pressure of 2,000 to 3,000 L of liquidSartorius Flexsafe New PE Film document. Reference 3 https://api.sartorius.com/document-hub/dam/download/5807/Flexsafe-New-PE-Film-Benchmark-Brochure-en-B-SPT1503-Sartorius.pdfSourced
That antioxidants are needed to keep the film stable and protect the polymer during extrusion and gamma irradiation; that optimising and tightly controlling their concentration is critical. That phosphite antioxidant is limited in S80 and not included in the contact layer of S71 (EVA-based). That without control of additives, bag age can affect cell growth. Extraction with water and ethanol, and cell-growth testing on irradiated bagsSartorius white paper (2020). Reference 4 https://www.sartorius.com/download/13284/white-paper-cellgrowth-flexsafe-flexboy-spt1103-e-data.pdfSourced
That bDtBPP is strongly detrimental to cell growth. That it is a breakdown product of Irgafos 168 (tris(2,4-di-tert-butylphenyl) phosphite), which is present in many polyethylene formulations. That it is harmful at concentrations well below the ppm level. That migration depends on time and temperature. That exposure of oxidised Irgafos 168 to ionising radiation was suggested as an important condition. The statement that replacing stainless-steel tanks with disposable bags brings significant environmental and cost advantagesHammond et al. 2013 (PubMed abstract). Reference 5 https://pubmed.ncbi.nlm.nih.gov/23569073/Sourced
The title of USP <665>, and the statement that it is an informational chapter that does not apply as a compendial requirement unless specified by a regulatory or enforcement authorityUSP <665> official page. Reference 6 https://doi.usp.org/USPNF/USPNF_M11135_02_01.htmlSourced
The title of USP <1665> (characterisation and qualification of plastic components and systems)USP <1665> official page. Reference 7 https://doi.usp.org/USPNF/USPNF_M11136_02_01.htmlSourced
The definitions of leachables and extractables. That the scope includes cell and gene therapy products. The three stages of risk assessment and example measures. That extraction studies on manufacturing components should be designed for the worst case (smallest scale, longest contact, highest temperature and pressure). That manufacturing components carry lower risk than packaging because of short contact times and a large volume relative to surface area. That upstream leachables may be removed downstream. Cumulative risk assessment. That risk is acceptable if all peaks are at or below the AET and there is no Class 1 leachable. That the draft was published at Step 2 on 1 August 2025ICH Q3E draft. Reference 8 https://database.ich.org/sites/default/files/ICH_Q3E_EWG_Step2_DraftGuideline_2025_0704.pdfSourced
That the final version of Q3E (Step 4) is scheduled for June 2027A schedule stated in the ICH Q3E work plan, not a settled fact. Reference 9 https://database.ich.org/sites/default/files/ICH_Q3E_EWG_WorkPlan_2024_0214.pdfNot yet confirmed
That BioPhorum updated its protocol on 22 April 2020, dropping 5 M sodium chloride and 1% polysorbate 80, time-zero sampling and elemental analysis of the 50% ethanol extract, cutting the testing burden by 30 to 50%, and introducing the extractables ecosystemBioPhorum published page. Reference 10 https://www.biophorum.com/download/extractables-testing-of-polymeric-single-use-components-used-in-biopharmaceutical-manufacturing/Sourced
The equipment-construction requirement that contact surfaces shall not be reactive, additive or absorptive21 CFR 211.65(a). Reference 11 https://www.ecfr.gov/current/title-21/chapter-I/subchapter-C/part-211/subpart-D/section-211.65Sourced
The requirements for equipment cleaning and maintenance and their written procedures (responsibility, schedules, methods, removal of previous batch identification and so on)21 CFR 211.67. Reference 12 https://www.ecfr.gov/current/title-21/chapter-I/subchapter-C/part-211/subpart-D/section-211.67Sourced
That water use is mainly associated with CIP and SIP and is a major environmental burden. That producing purified water and water for injection, and cleaning and sterilisation, are energy-intensive. That CIP and SIP accounted for more than 85% of total water use in one perfusion process. That the paper covers stainless-steel facilities and excludes the manufacture of consumables from its scopeBunnak et al. 2016. Reference 13 https://pmc.ncbi.nlm.nih.gov/articles/PMC5082523/Sourced
That moving to disposable equipment is expected to reduce environmental impactAn expectation stated in the conclusion of Bunnak et al. 2016, not a result assessed in that paper. Reference 13 https://pmc.ncbi.nlm.nih.gov/articles/PMC5082523/Not yet confirmed
That stainless-steel tanks have dominated large-scale manufacturing (1,000 to more than 25,000 L). That fixed equipment is costly and slow to install and qualify. That disposables allow faster design changesLi et al. 2010 review. Reference 14 https://pmc.ncbi.nlm.nih.gov/articles/PMC2958569/Sourced
Lower cross-contamination risk and shorter lead times as advantages of single-use tanks. That reusable tanks are regarded as the gold standard because their geometry is well understood. That single-use tanks differ in shape, agitation principle and aeration, which can make transfer and scale-up a challenge. The 50 to 2,000 L family, H/D 2:1Dreher et al. 2013. Reference 15 https://pmc.ncbi.nlm.nih.gov/articles/PMC3980816/Sourced
That DynaDrive runs from 5 L to 5,000 L, is described as the first 5,000 L single-use bioreactor on the market, and can use Aegis5-14 film for its bagsThermo Fisher product page (a statement about its own product). Reference 16 https://www.thermofisher.com/us/en/home/bioprocessing/products/bioreactors/single-use-dynadrive.htmlSourced
That the wave-type bioreactor is disposable and needs no cleaning or sterilisationSingh 1999 (abstract). Reference 17 https://pmc.ncbi.nlm.nih.gov/articles/PMC3449934/Sourced
That physical constraints limit the maximum P/V in large single-use tanks to around 20 to 30 W/m³Lemire et al. 2026. Reference 18 https://pmc.ncbi.nlm.nih.gov/articles/PMC12908111/Sourced
Layer thicknesses (contact layer about 264 µm, EVOH about 25 µm, contact layer about 74%). That the roughly 0.016 mmol of oxygen passing through 1 m² per day equals about 13 seconds' worth for 1 L of culture at 20 million cells/mL. Wetted area per mL of liquid (0.60 cm²/mL at 1 L, 0.048 cm²/mL at 2,000 L, about 12.6 times). Hydrostatic pressure of about 21 kPa at the bottom of a 2,000 L bagOur calculation. 1 mil = 25.4 µm, 22.4 L/mol, oxygen uptake of 5.5 pmol/cell/day, a completely filled cube, a cylinder with H/D = 2 and a density of 1,000 kg/m³ are assumptions set by this articleOur calculation
The full text, test conditions and official dates of USP <665> and <1665>. The layer structures of other companies' films. An overall comparison of environmental impact including the manufacture and disposal of single-use componentsNot stated because the text is for subscribers and was not checked, or because it could not be confirmed in primary sources within the scope of this article (commentary)Commentary
The reading that the gas barrier protects quality during storage. The framing that gamma sterilisation is a step that changes the chemistry of the material. The framing that the supplier's process control is the price of entry. The reading that reuse of standardised data makes replacement harder. The reading that on-site detectable defects get coarser with volume, so the process capability of not creating defects matters. The point that the 21 CFR 211.65 requirement is the same for stainless steel and polymer. That used components become solid waste. The organisation of the comparison tableThis article's own framing and commentary based on published content. Not views expressed by the companies or institutionsCommentary
That Figs. 1 to 5 are explanatory drawings, not real product cross-sections or measurement results. That the layer thickness ratios on the right of Fig. 1 are an equal-split schematic. That the hero image and Fig. 6 are AI-generated imagesA note by this article (commentary)Commentary

Last updated 23 September 2026. Sources are limited to primary material (film and equipment makers' documents on their own products, peer-reviewed papers, and published material from ICH, USP, the US Code of Federal Regulations and BioPhorum). Makers' documents are treated only as statements about that company's own products. The full text and official dates of USP <665> and <1665>, the layer structures of other companies' films, and an overall comparison of environmental impact including the manufacture and disposal of single-use components are not covered, because they could not be confirmed in published primary sources. ICH Q3E is at the draft (Step 2) stage. All figures are explanatory concept graphics. Figs. 1 to 5 are vector drawings; the hero image and Fig. 6 are AI-generated images, and none of them shows a real product cross-section or an actual product.

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