
Volatile Organic Compounds (VOCs) are chemical compounds that have a high vapour pressure, causing them to evaporate and release molecules into the air. They are emitted from a variety of sources, including plastic products, and can have harmful effects on both the environment and human health. The presence of plastic products indoors has the potential to impact indoor air quality, and the release of VOCs from plastics has been linked to stimulation and damage to the human body. While the specific effects of VOCs on plastic curvature are not explicitly mentioned in the sources, it is evident that VOC emissions from plastics are a significant area of concern, with ongoing research focused on understanding their potential impact on human health and the environment.
| Characteristics | Values |
|---|---|
| VOCs cause plastic to curve | No evidence found |
| VOCs are released from | Polymeric materials, plastic debris, plastic products, plastic tracks, and consumer products |
| Impact of VOCs | Harmful to the environment and human health |
| Factors affecting VOC emissions | Temperature, relative humidity (RH), and air exchange rate (AER) |
| Examples of VOCs | Phthalates, formaldehyde, benzene, acrolein, propanal, methyl vinyl ketone, and methyl propenyl ketone |
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What You'll Learn

Plasticisers and flame retardants
Volatile Organic Compounds (VOCs) are released from polymeric materials, such as plastics, due to their high vapour pressure. VOCs are commonly emitted from plasticisers and flame retardants added to enhance polymeric materials. For instance, phthalates like bis(2-ethylhexyl)phthalate (DEHP) are often incorporated into poly(vinyl chloride) (PVC) as a plasticiser. Emission levels of VOCs can vary over time due to factors like thermal stress and UV radiation.
Flame retardants are chemical compounds added to plastics to prevent, delay, or slow down combustion, reduce smoke formation, and prevent melt collapse. They work by interfering with or eliminating one of the key ingredients required for combustion (fuel, oxygen, or an ignition source). The most common type of flame retardant is halogenated compounds, including brominated and chlorinated varieties. These halogenated flame retardants are highly effective even at low load levels. During a fire, these compounds thermally degrade, releasing hydrogen chloride and hydrogen bromide, which react with the free radicals in the flame. This process forms less reactive free radicals, reducing the volume of reactive gases available for combustion and slowing it down.
Non-halogen flame retardants, such as intumescents (phosphorus-based) and metallic oxides, are also available but require higher load levels and may need adjustments to maintain the mechanical properties of the plastic. One example of a non-halogen flame retardant is solid char-formation, which creates a thick layer of carbon char on the plastic's surface during a fire, acting as a barrier that interrupts combustion. Another class of non-halogen flame retardants includes metallic oxides and hydrated minerals, such as aluminium and magnesium hydroxides, which use endothermic reactions to remove heat and release water molecules, cooling the plastic and limiting the formation of reactive gases.
Plasticisers are another type of additive commonly used in plastics. Phthalic acid esters and phosphororganic compounds (POC) are frequently used as plasticisers in commercial products. These compounds are released into the indoor environment and can accumulate in air and dust, leading to potential inhalation and ingestion risks, especially for young children.
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Temperature-driven variations in VOC emissions
Volatile Organic Compounds (VOCs) are known for their high vapour pressure, which causes them to evaporate and release molecules into the air. The emission levels of VOCs can vary due to factors like thermal stress and ultraviolet (UV) radiation.
A study on temperature-driven variations in VOC emissions from plastic products and their fate indoors exposed plastic samples to increasing temperatures (between 18 and 28 °C) in controlled environmental chambers. The results indicated a positive association between temperature and plastic emissions, with almost all selected VOC emissions displaying a linear relationship with temperature. The highest-emitting polymer per surface area was PS tubing plastic. Formaldehyde concentrations increased by 29% and 31.6% relative to the baseline conditions at 18°C and 28°C, respectively.
The impact of temperature on VOC emissions was also observed in a study by Royer et al. (2018), who found that low-density polyethylene (LDPE) incubated at ambient outdoor temperatures produced varying amounts of CH4, C2H4, C2H6, and C3H6. Additionally, they reported an increase in the VOCs production rate as the surface-to-volume ratio increased, suggesting that VOC release may continue as long as the plastic remains exposed to thermal degradation conditions.
The sensitivity of VOC emissions to ambient temperature is not limited to plastics but also applies to anthropogenic VOCs (AVOCs) and biogenic VOCs (BVOCs). Studies have shown that high ambient temperatures significantly increase AVOC emissions from petrochemical processing, vehicles, and the use of solvents. Similarly, the release of VOCs from vegetation, or BVOCs, is temperature-dependent and controlled by vegetation composition, with different plant species releasing distinct amounts of VOCs.
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Environmental factors on the emission of VOCs
Volatile Organic Compounds (VOCs) are emitted as gases from certain solids or liquids. They are named for their high vapour pressure, which causes them to evaporate and release molecules into the air. VOCs are naturally occurring in the environment, but human activities have dramatically increased their emission in recent decades. VOCs are emitted by thousands of products, including paints, varnishes, cleaning products, fuels, and plastics.
Environmental Factors Affecting VOC Emissions
The emission of VOCs is influenced by various environmental factors, particularly temperature, relative humidity (RH), and air exchange rate (AER). These factors interact with the specific properties of the material emitting VOCs, such as its hardness and chemical composition.
Temperature plays a significant role in VOC emissions. Studies have shown that higher temperatures promote the release of VOCs from plastics. For example, waste plastics released about 500 μg/g of VOCs at 200 °C. Additionally, the production rate of VOCs increased with a higher surface-to-volume ratio, indicating that VOC emissions may continue throughout the lifetime of plastics under certain conditions.
Relative humidity (RH) also impacts VOC emissions. As RH increases, the concentration of different VOCs tends to increase as well. However, RH does not affect the concentration percentage of VOCs in the total VOC content.
Air exchange rate (AER) is another critical factor. Increasing the AER significantly reduces the concentrations of VOCs. For instance, when the AER was increased, the concentration of specific VOCs, such as calkane and oxygenated organic compounds, decreased substantially.
The properties of the emitting material also play a role. Softer polymers tend to emit broader and higher VOC profiles than harder plastics. Additionally, the chemical properties of the material can interact with VOCs, leading to varying emission profiles. For example, phenol emissions from a standard plate increased over 28 days, while emissions from a sample with specific chemical properties decreased over the same period.
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VOC emissions from consumer products
Volatile Organic Compounds (VOCs) are known for their high vapour pressure, which causes them to evaporate and release molecules into the air. VOCs are released from polymeric materials, such as plastics, and can have detrimental effects on the environment and human health. The release of VOCs from plastic degradation is a growing concern, with littered face masks contributing significantly to environmental pollution.
Consumer products made from polymers can emit VOCs, and the softness of the polymers impacts the VOC emission levels. Softer polymers emit a broader and higher range of VOCs than harder plastics. The type of material also influences the emission profile, as seen with the differing rates of phenol and acetophenone emissions from polyurethane and foam samples.
To address the impact of VOC emissions, directives have been implemented to limit VOC content in specific products, such as decorative paints, varnishes, and vehicle refinishing products. These directives aim to mitigate the negative environmental and health effects associated with VOC emissions. Additionally, there is a focus on reducing emissions from industrial installations and activities that contribute significantly to VOC pollution.
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VOCs from photo-degraded plastic debris
Volatile Organic Compounds (VOCs) are named for their high vapour pressure, which causes them to evaporate and release molecules into the air. VOCs are the primary pollutant emitted by chemical laboratories, causing significant damage to the environment and posing a serious threat to human health. The release of toxic VOCs is a potential hazard associated with the environmental weathering of plastic debris.
The emissions of VOCs from degraded plastic debris and microplastics have been a topic of interest. A study by Lomonaco et al. investigated the generation of nanofibers from meltblown face mask filters (MB filters) and their adverse effects on soil species, such as earthworms and springtails. The results suggested inhibited reproduction and stunted growth in springtails, decreased intracellular esterase activity in earthworm coelomocytes, and inhibited spermatogenesis in male earthworm reproductive tissues.
Another study by Royer et al. demonstrated that environmentally-aged low-density polyethylene (incubated at ambient outdoor temperatures) produced varying amounts of CH4, C2H4, C2H6, and C3H6. They also reported an increase in the VOCs production rate with an increasing surface-to-volume ratio, indicating that VOCs release may continue throughout the lifetime of plastics exposed to thermal and/or photo-oxidative degradation.
A progressive increase in VOCs was observed during artificial photo-degradation, with a chemical profile that included carbonyls, lactones, esters, acids, alcohols, ethers, and aromatics. All samples of plastic debris collected at a marine beach released harmful compounds, such as acrolein, benzene, propanal, methyl vinyl ketone, and methyl propenyl ketone. These findings support the hypothesis that microplastics represent an unrecognized source of environmental pollution.
The development of analytical procedures for determining VOCs released during the degradation process of plastic debris is crucial. One such method combines headspace (HS) sampling, needle trap microextraction (NTME), and gas chromatography/mass spectrometry (GC–MS). This procedure has been used to monitor the release of VOCs from micronized polymer powders and investigate macro- and microplastic marine debris.
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Frequently asked questions
VOCs are Volatile Organic Compounds, which are named for their high vapour pressure, causing them to evaporate and release molecules into the air.
VOC emission levels from plastics can vary due to factors like thermal stress and UV radiation. VOC emissions from plastics have been shown to increase with temperature. However, there is no mention of whether these emissions cause plastics to curve.
VOCs released from plastics are a source of environmental pollution and can have harmful effects on ecosystems and human health.
Some VOCs emitted from plastics include carbonyls, lactones, esters, acids, alcohols, ethers, aromatics, acrolein, benzene, propanal, and methyl vinyl ketone.
Increasing the Air Exchange Rate (AER) can help reduce VOC concentrations. Additionally, maintaining lower temperatures can minimize VOC emissions, as they have a positive relationship.









































