What Is CaO Use in Plastic Recycling and Why Is It Needed?
The use of CaO in plastic recycling means adding a certain proportion of quicklime (calcium oxide, CaO) to recovered polymer feedstock before or during extrusion. This method converts the moisture trapped inside the polymer into calcium hydroxide (Ca(OH)₂) through a chemical reaction and eliminates production defects caused by evaporation.
Although plastics pass through washing, mechanical squeezing and hot-air drying stages during the recycling process, a residual moisture of typically 0.1–0.5% can remain on the granule surface and in its micro-pores. Conventional hot-air dryers struggle to go below this level; the moisture profile varies significantly from batch to batch, especially in PCR (post-consumer recycled) feedstock. Seasonal changes, storage conditions and wash-water quality directly affect the moisture content. The CaO-based solution overcomes this critical threshold chemically rather than by physical drying; it has therefore become a standard technique on post-consumer recycling lines.
Another important advantage of the method is that it can be applied without changing the line's existing infrastructure. Powdered CaO can be added directly to the main hopper or to a side-dosing unit, while the masterbatch form can be introduced to the line through standard granule feeding. The new investment cost is minimal and the payback period is typically expressed in weeks.
In the Turkish plastics industry, demand for lime-based solutions has risen sharply with the increasing PCR ratio, especially in packaging, construction and agricultural applications. Because manufacturers are under pressure to use recovered feedstock without reducing line efficiency, chemical moisture-scavenger solutions are coming to the fore.

The Moisture Problem in Recycled Polymers and Production Losses
The most common problem in processing recycled feedstock is the micro-bubbles, fisheyes and surface cracks that appear on the extrusion line. The root cause of these defects is almost always water trapped inside the polymer; even after washing, it is impossible for the granule mass to be completely dry.
The water molecules inside the polymer, heated to 200–250 °C in the extruder screw, turn into vapor. At the die exit, where the melt stream passes from the high-pressure zone to atmospheric pressure, this water vapor suddenly expands and leaves pores. The consequences are clear: surface defects (matt spots, pits, bubbles), a drop in tensile strength and impact resistance, color distribution defects in formulations mixed with masterbatch, slower production speed and a higher scrap rate. This is accompanied by filter clogging, mold wear and increased line stoppages.
Vented (vacuum-degassing) extruders partly solve this problem; however, the load on the vacuum lines increases, energy consumption rises and maintenance frequency tightens. The use of CaO in plastic recycling can increase production speed by an average of 5–15% by reducing the load on the vacuum system; relevant industry reports document this approach as an efficiency gain. The direct financial impact for manufacturers is reduced scrap and increased line speed. In addition, because the pre-drying time is shortened, electricity consumption also falls. In modern recycling plants, the first measure taken when the scrap rate exceeds 3% is to add a moisture scavenger to the dosing line.



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The Chemical Mechanism of CaO Use in Plastic Recycling
Quicklime (CaO), when it meets water, undergoes a stable hydration reaction:
CaO + H₂O → Ca(OH)₂ + heat (≈64 kJ/mol)
When this reaction takes place inside the polymer melt, four things happen simultaneously. First, the residual water is converted into calcium hydroxide, a stable and solid compound; it does not remain in liquid or gaseous form. Second, since no water molecule is left to evaporate, no bubbles form. Third, the reaction product Ca(OH)₂ behaves like a fine-grained filler in the polymer matrix and typically does not adversely affect the mechanical properties; on the contrary, through a nucleation effect it can improve the crystallization balance in some applications. Fourth, the heat released by the reaction is too small to affect the extrusion profile and creates no temperature management problem.
In halogenated polymers (PVC, PE/PP blends containing brominated flame retardants), acidic by-products such as HCl are released during processing. This is where the second function of CaO and Ca(OH)₂ — acid scavenging — comes into play:
Ca(OH)₂ + 2HCl → CaCl₂ + 2H₂O
In this way, the use of CaO in plastic recycling simultaneously controls polymer chain degradation caused by both moisture and corrosive by-products. The thermal stability time is extended, the corrosion life of extruders and molds increases, and odor intensity decreases. This dual-function mechanism distinguishes CaO from an ordinary moisture absorber and makes it valuable especially on mixed-stream PCR lines.

The Role of Quicklime, Moisture Scavenger and Gas Remover Solutions in the Process
In the formulation of recycling plants, lime-based solutions are generally evaluated as three different product categories and are integrated into the CaO-in-plastic-recycling scenario either together or on their own.
Quicklime (CaO): Micronized, high-reactivity and low-impurity CaO is added directly to the polymer melt or to the masterbatch pre-mix. The typical particle size is in the 5–45 micron range; micronized products at the D₉₀ ≤ 20 micron level are preferred on PE film and injection lines. When impurities such as iron and magnesium are kept low, the color and mechanical strength of the final product are preserved. It is generally used at 2–10% (phr). Because its reactive surface area is high, at the same dosage it binds moisture far faster than classic calcium carbonate filler; this delivers a large effect with small dosages.
Moisture scavenger (lime-based desiccant): This is the "desiccant masterbatch" form in which quicklime CaO is compounded with a polyethylene or polypropylene carrier resin. When masterbatch is preferred over pure powdered CaO, dosing is done more homogeneously with automatic feeding, operator contact risk decreases, storage safety increases and dust emission is eliminated. In recovered HDPE, LDPE and PP, a 1–3% dosage enables the trouble-free processing of feedstock with a moisture content of 0.3–0.5%. This is the most practical solution to micro-bubble and fisheye problems. Because the product's matrix is compatible with the recycled feedstock, no additional compatibilizer is needed; it is fed trouble-free on the same line as color masterbatches.
Gas remover (acid/odor-absorbing lime): In mixed waste plastics and PVC-heavy recycling, HCl, malodorous compounds, mercaptans and VOCs can be released during thermal decomposition. Lime-based gas-remover products chemically bind these by-products and reduce the amount of gas loaded onto the extruder ventilation system. As of 2026, with environmental emission limits tightening, these products are seen to be preferred in the polymer process as well, similarly to their performance in flue gas desulfurization. They provide a marked improvement in operator working conditions and stack emissions; they constitute a significant advantage in occupational health and safety audits.
Depending on the need, a single product may be sufficient, while in complex formulations more than one lime-based solution is used together. For example, in high-moisture post-consumer PE granules, a moisture-scavenger masterbatch and gas-remover support can be applied together; in PVC profile recycling, a hydrated lime (Ca(OH)₂)-based acid scavenger is preferred together with micronized CaO. In the decision-making process, feedstock analysis (moisture content, chlorine content, odor threshold, iron impurity) serves as a direct guide.

Technical Points to Consider in Application
The success of CaO use in plastic recycling depends on four main parameters: particle size, reactivity, purity and dosage. The typical ranges of these parameters can be summarized as follows: particle size (D₉₀) 5–20 microns, reactivity (t₆₀) 1–3 minutes, CaO purity ≥90% and dosage 1–10% (phr); the packaging, meanwhile, must be airtight and dry.
Reactivity control is of critical importance. The HCl-consumption-into-water test (t₆₀) compliant with the TS EN 459-2 standard measures the moisture-capture speed of CaO. In the plastics application, a t₆₀ value of less than 3 minutes is necessary for the reaction to be completed during the short residence time inside the extruder. Low-reactivity lime exits the die at the extrusion outlet without having reacted and does not deliver the desired result; this creates low quality and a misleading cost advantage.
When determining the dosage, the feedstock's moisture profile should be measured by Karl Fischer titration, and theoretically about 0.3 phr of CaO should be introduced for every 0.1% of moisture. In practice, the dosage is fine-tuned with small-scale trials on the production line; these trials are evaluated through line speed, vacuum load and scrap rate. Overdosing causes graying of the product color and a slight drop in mechanical strength; insufficient dosing causes unwanted bubbling. On the purity side, high iron oxide and magnesium oxide impurities create a risk of yellowing, especially in transparent or light-colored products; for this reason, reference values of CaO content ≥90% and Fe₂O₃ ≤0.2% are used for the plastics application.
On the storage side, quicklime (CaO) reacts rapidly with moisture in the air. For this reason, packaging must be kept airtight and stored on pallets in a dry, cool environment (preferably <50% relative humidity). Open packaging can lose a significant part of its activity within 24 hours; in masterbatch-form products, the polymer shell extends this period and raises the shelf life to typically 12 months.
A simple quality check on the line quickly confirms that the dosage has been chosen correctly: in a 5-minute production sample, the number of fisheyes, bubble density and surface gloss are inspected visually; if necessary, microstructure analysis is performed by SEM.

Good Practice Examples in the Recycling Sector as of 2026
Under the European Green Deal and Türkiye's Zero Waste Regulation, post-consumer recycling rates are expected to increase as of 2026. As the PCR ratio rises, the moisture and contamination profile of the feedstock used becomes more challenging. This challenge directly increases the importance of CaO use in plastic recycling. The following approaches are observed in good-practice examples in the field:
On PCR PE film lines, micronized CaO or a moisture-scavenger masterbatch is added to the main hopper at 2%; the load on the vacuum line falls by an average of 30–40% and the number of fisheyes decreases markedly. In PVC profile recycling, a calcium-based acid scavenger is introduced as a co-stabilizer alongside the main stabilizer package in the 0.5–1 phr range; this brings HCl-induced yellowing and thermal degradation under control. In mixed plastic granule production, a gas remover is preferred at 1–2% to reduce malodor and HCl emissions; it helps maintain in-plant air quality standards. Because moisture sensitivity is very high in the recycling of engineering plastics (PA, PBT), the CaO dosage is used in the 0.5–1 phr range, in a pinpoint manner and usually in moisture-scavenger masterbatch form.
In conclusion, although CaO use in plastic recycling may look like a simple moisture-absorber solution on paper, when selected with the right product, the right particle size, the right reactivity and the right dosage, it is a critical engineering choice that visibly lowers scrap and energy costs and raises the technical standards of recovered feedstock. In terms of both technical performance and regulatory compliance, having a CaO-based solution in the formulation toolbox of a modern recycling plant is now regarded as a necessity rather than a preference. With the right supplier selection, continuous quality control and feedstock-specific dosage calibration, this necessity can be turned into a lasting competitive advantage. A review of the technical data sheet with the supplier, sample testing from batches, and a three-to-four-batch pilot study in the field are sufficient to determine the right product-dosage combination.







