Cigarette filters, along with cigarette paper, ink, capsules and adhesives, are part of a filter cigarette. The filter may be made from cellulose acetate fibre, paper or activated charcoal (either as a cavity filter or embedded into the cellulose acetate). Macroporous phenol-formaldehyde resins and asbestos have also been used in cigarette filters. The acetate and paper modify the particulate smoke phase by particle retention (filtration), and finely divided carbon modifies the gaseous phase (adsorption). Filters can reduce "tar" and nicotine smoke yields up to 50%, with an greater removal rate for other classes of compounds (e.g., phenols), but are ineffective in filtering toxins such as carbon monoxide. Most factory-made cigarettes are equipped with a filter; those who roll their own can buy them from a tobacconist.
From 1935, a British company began to develop a machine that made cigarettes incorporating the tipped filter. It was considered a speciality item until 1954, when manufacturers introduced the machine more broadly, following a spate of speculative announcements from doctors and researchers concerning a possible link between lung diseases and smoking. Since filtered cigarettes were considered "safer", by the 1960s, they dominated the market. Production of filter cigarettes skyrocketed from 0.5 percent in 1950 to 87.7 percent by 1975.
Cellulose acetate is made by esterifying bleached cotton or wood pulp with acetic acid. Of the three cellulose hydroxy groups available for esterification, between two and three are esterified by controlling the amount of acid (degree of substitution (DS) 2.35-2.55). The ester is spun into fibers and formed into bundles called filter tow. Flavors (menthol), sweeteners, softeners (triacetin), flame retardants (sodium tungstate), breakable capsules releasing flavors on demand, and additives colouring the tobacco smoke may be added to cigarette filters. The five largest manufactures of filter tow are Hoechst-Celanese and Eastman Chemicals in the United States, Rhodia Acetow in Germany, Daicel in Japan, and Courtaulds in the United Kingdom.
Starch glues or emulsion-based adhesives are used for gluing cigarette seams. Hot-melt and emulsion-based adhesives are used for filter seams. Emulsion-based adhesives are used for bonding the filters to the cigarettes.
In the 1970s epidemiologic evidence relative to tobacco-related cancers and data for coronary heart disease have indicated a reduced risk among filter smokers for these diseases. Between 1970 and 1980 some studies showed a 20-50 % reduction in risk of lung cancer for long-term smokers of filter cigarettes as compared to smokers of non-filter cigarettes (IARC, 1986) but later studies indicated a similar risk for lung cancer in smokers of filter and non-filter cigarettes.
Various add-on cigarette filters ("Water Pik", "Venturi", "David Ross") are sold as stop-smoking or tar-reduction devices. The idea is that filters reduce tar-nicotine levels permitting the smoker to be weaned away from cigarettes.
The tobacco industry has reduced tar and nicotine yields in cigarette smoke since the 1960s. This has been achieved in a variety of ways including use of selected strains of tobacco plant, changes in agricultural and curing procedures, use of reconstituted sheets (reprocessed tobacco leaf wastes), incorporation of tobacco stalks, reduction of the amount of tobacco needed to fill a cigarette by expanding it (like puffed wheat) to increase its "filling power", and by the use of filters and high-porosity wrapping papers. However, just as a drinker tends to drink a larger volume of beer than of wine or spirits, so many smokers tend to modify their smoking pattern inversely according to the strength of the cigarette being smoked. In contrast to the standardized puffing of the smoking machines on which the tar and nicotine yields are based, when the smoker switches to a low-tar, low nicotine cigarette, he smokes more cigarettes, takes more puffs and inhales more deeply. Conversely, when smoking a high-tar, high-nicotine cigarette there is a tendency to smoke and inhale less.
In spite of all changes in cigarette design and manufacturing over the last 50 years, the use of filters and "light" cigarettes did neither decrease the nicotine intake per cigarette, nor did it lower the incidence of lung cancers (NCI, 2001; IARC 83, 2004; U.S. Surgeon General, 2004). The shift over the years from higher- to lower-yield cigarettes may explain the change in the pathology of lung cancer. That is, the percentage of lung cancers that are adenocarcinomas has increased, while the percentage of squamous cell cancers has decreased. The change in tumor type is believed to reflect the higher nitrosamine delivery of lower-yield cigarettes and the increased depth or volume of inhalation of lower-yield cigarettes to compensate for lower level concentrations of nicotine in the smoke.
Cellulose acetate is non-toxic, odorless, tasteless, and weakly flammable. It is resistant to weak acids and is largely stable to mineral and fatty oils as well as petroleum. It is biodegradable and the raw material is a renewable natural polymer expected to find application for other uses in the future. Smoked cigarette butts contain 5–7 mg nicotine, children ingesting >2 whole cigarettes, 6 cigarette butts or a total of 0.5 mg/kg of nicotine should be admitted to a hospital. Cellulose acetate is hydrophilic and retains the water-soluble smoke constituents, of which many are irritating (acids, alkali, aldehydes, and phenols), while letting through the lipophilic aromatic compounds.
Atmospheric moisture, gastric acid, light, and enzymes hydrolyze cellulose acetate to acetic acid and cellulose. Cellulose may be further hydrolyzed to cellobiose or glucose in an acidic medium, and eventually form valuable humus. Humans cannot digest cellulose and excrete the fibers in feces. Like wood, paper and cotton, cigarette filters in soil rot slowly over months to years.
Cigarette butts are the most common form of anthropogenic (man-made) litter in the world, as approximately 5.6 trillion cigarettes are smoked every year worldwide. Of those it is estimated that 4.5 trillion cigarette butts become litter every year.
Many governments have sanctioned stiff penalties for littering of cigarette filters; for example the Washington state imposes a penalty of $1,025 for littering cigarette filters. Another option is developing better biodegradable filters, much of this work lies heavily on the research in the secoundary mechanism for photodegradtion as stated above. The next option is using cigarette packs with a compartment to discard cigarette butts in, implementing monetary deposits on filters, increasing the availability of butt receptacles, and expanding public education. It may even be possible to ban the sale of filtered cigarettes altogether on the basis of their adverse environmental impact. Recent research has been put into finding ways to utilizes the filter waste, to develop a desired product. One research group in South Korea have developed a simple one-step process that converts the cellulose acetate in discarded cigarette filters into a high-performing material that could be integrated into computers, handheld devices, electrical vehicle and wind turbines to store energy. These materials have demonstrated superior performance as compared to commercially available carbon, graphene and carbon nano tubes. The product is showing high promise as a green alternative for the waste problem. Another group of researchers has proposed adding tablets of food grade acid inside the filters. Once wet enough the tablets will release acid that accelerates degradation to around two weeks (instead of using cellulose triacetate and besides of cigarette smoke being quite acidic).
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