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Dry cleaners

Design

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What is PERC?

Perchloroethylene (aka tetrachloroethylene or PERC) is the main chemical found in products used for dry cleaning worldwide. It acts as a solvent to remove stains from all types of fabrics, since it is an excellent solvent for organic materials. It is volatile, highly stable and non-flammable, reasons for which it is so widely used in this industry. The big selling point of this chemical is that it is quite effective and quite cheap, which means that almost all dry cleaners throughout the globe use it daily.
The problem is that PERC is quite toxic, both for humans and the environment. Like many other chlorinated hydrocarbons, PERC acts as a central nervous system depressant, and due to its volatile character, it can enter the body through both the respiratory system and dermal exposure. The World Health Organisation’s International Agency for Research on Cancer lists it as being a group A2 carcinogen, which means that it is “probably carcinogenic to humans”. It can also dissolve fats from the protective layer of the skin, potentially resulting in skin irritation. Animal studies have already shown evidence that exposure to PERC increases the risk of developing Parkinson’s disease in ninefold, and the compound has been shown to cause liver tumours in mice, and kidney tumours in rats. PERC is also labelled as toxic for the environment, since its degradation is quite slow, having an estimated atmospheric half-life of 100 days.

The predominant routes of exposure to PERC for the general population are the inhalation of the compound from both ambient and indoor environments, and ingestion, by drinking water contaminated with it. People working on the dry cleaning industry are, of course, exposed to higher levels of PERC than the general population, and, in addition, people residing near dry cleaning locations are also exposed to high levels, due to the volatile nature of the compounds and to vapour intrusion.

Because of all these reasons, the French government has set up for 2022 the complete banning of PERC from dry cleaning establishments situated close to residential areas. Similar laws had been already passed in Denmark and the USA.

Figure 1: Effects of PERC on the human body. PERC’s mechanism of toxicity differs from tissue to tissue. The main two targets of PERC, in the human body, are neurological tissues and hepatic tissues.
In the case of the neurological effects, experimental studies in rodents have shown that PERC alters the fatty acid pattern of the brain’s phospholipids and amino acids. This explains its neurotoxic effects. Other studies propose that PERC might be incorporated into the brain membranes, hence altering the neural conduction velocity. PERC can also interfere with the voltage-gated channels and neuronal receptors of the nervous cells. Shafer et al. (2005) showed that PERC disturbs whole-cell calcium currents as well.
In contrast with these neurological effects, which are a result of PERC itself, the hepatic effects are a result of oxidative metabolites including trichloroacetic acid and dichloroacetic acid, which accumulate on the liver.

Figure 2: Effects of PERC on the environment. PERC is a compound that tends to volatise quickly when released into water or soil. Furthermore, it is also mobile in soil and therefore has the potential of leaching bellow the soil surface and reaching groundwater, hence contaminating it. The United States’ Health and Human Services identified PERC in approximately 4% of aquifers in the latest US Geological Survey, showing that aquifer contamination is indeed a problem.
It can biodegrade to tricholoethylene, dichloroethylene, vynil chloride or ethane through dechlorination, but these compounds are not safer than PERC itself.

What are the existing alternatives to PERC?

There are already some existing alternatives to the use of PERC in dry cleaning, but the scientific community is divided regarding their safety.

The first alternative is the use of liquid silicon instead of PERC. Silicon is a commonly used solvent, which we find in products such as cosmetics, deodorants and shampoos. It is both odourless and colourless making it in theory a perfect alternative to PERC. However, some scientists have expressed their concern over the use of this chemical since no complete analysis of its impact on humans has been performed to date. Furthermore, only some countries, such as Canada and the UK, have declared liquid silicon as not harmful for the environment, which shows that there is no global consensus on its safety. Furthermore, the European Chemical Agency has reported that liquid silicone is bioaccumulative. It is very difficult to break down and it is likely to accumulate in our bodies, which is why the EU’s Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) has called for further research.

Another existing alternative is wet cleaning. This method involves the use of gentle washing machines, water, biodegradable soaps and conditioners, and various types of pressing and re-shaping equipment specialised for different types of fabric and fibre types. This method is quite expensive because it requires the investment of acquiring different machines for different fabrics, and requires a lot of training for the operators.
Although a safe alternative for the environment, the specialised detergents and conditioners are mild and not as effective on getting rid of all stains, and many tailors do not recommend it as the process can harm sensible garments.

Another existing alternative is the use of KWL as a solvent. KWL is a petroleum-based solvent, which means that its use is not environmental-friendly. Furthermore, recent studies show that KWL is slightly toxic for human health and also that it is highly inflammable.

Similar data is found for another alternative, the solvent K. This is also a petroleum-based solvent, and is highly inflammable as well. This hydrocarbon is also uncommonly volatile for a compound of its class, which makes it very efficient for dry-cleaning, but hazardous for human health.

How would our product fit in the market?

To understand how our team could make a positive impact on the dry cleaning industry, we interviewed all the dry cleaners in Paris to gather information about the use of PERC and on the impact that the new rules will have on their businesses. For more detailed information on the questionnaire, visit our human practices page!

Overall, most dry cleaners expressed their concern about the compulsory changes, not only because of the economical impact of renewing their already established methods, but mainly because of their concern over the efficiency of the existing alternatives.

Those dry cleaners that had already made the change to the new alternatives told us that the new methods were highly less efficient than PERC itself, and that therefore they now were required to use pre-washing products specific to each type of stains. They also told us that amongst the most difficult stains to remove, red wine was a specially challenging one, especially on white and light coloured pieces of clothing.

We therefore decided to focus on red wine stains by trying to produce and enzymatic pre-washing product that would help washing the red wine stains away! For more information about the outline of our project, visit our pour project page!

Attributions

The study on PERC was performed by Alicia, Allison and Elisa.

References

• Public Health Statement for Tetrachloroethylene (PERC) from the Agency for Toxic Substances & Disease Registry of the United States Department of Health and Human Services (2014)
• Benane SG, Blackman CF, House DE. 1996. Effect of perchloroethylene and its metabolites on intercellular communication in clone 9 rat liver cells. J Toxicol Environ Health 48(5):427-437.
• Briving C, Jacobson I, Hamberger A, et al. 1986. Chronic effects of perchloroethylene and trichloroethylene on the gerbil brain amino acids and glutathione. Neurotoxicology 7:101-108.
• Dallas CE, Chen XM, Muralidhara S, et al. 1994a. Use of tissue disposition data from rats and dogs to determine species differences in input parameters for physiological model for perchloroethylene. Environ Res 67:54-67.
• Dallas CE, Chen XM, O’Barr K, et al. 1994b. Development of a physiologically based pharmacokinetic model for perchloroethylene using tissue concentration - time data. Toxicol Appl Pharmacol 128:50-59.
• Ghantous H, Danielsson BRG, Dencker L, et al. 1986. Trichloroacetic acid accumulates in murine amniotic fluid after tri- and tetrachloroethylene inhalation. Acta Pharmacol Toxicol 58:105-114.
• Hamada T, Tanaka H. 1995. Transfer of methyl chloroform, trichloroethylene and tetrachloroethylene to milk, tissues and expired air following intraruminal or oral administration in lactating goats and milkfed kids. Environ Pollut 87(3):313-318.
• Kyrklund T, Alling C, Kjellstrand P, et al. 1984. Chronic effects of perchloroethylene on the composition of lipid and acyl groups in cerebral cortex and hippocampus of the gerbil. Toxicol Lett 22:343-349.
• Kyrklund T, Kjellstrand P, Haglid K. 1987. Brain lipid changes in rats exposed to xylene and toluene. Toxicology 45:123-133.
• Kyrklund T, Kjellstrand P, Haglid KG. 1988. Effects of exposure to freon 11, 1,1,1-trichloroethane or perchloroethylene on the lipid and fatty-acid composition of rat cerebral cortex. Scand J Work Environ Health 14:91-94.
• Kyrklund T, Kjellstrand P, Haglid KG. 1989. Lipid composition and fatty acid pattern of the gerbil brain after exposure to perchloroethylene. Arch Toxicol 60:397-400.
• Kyrklund T, Kjellstrand P, Haglid KG. 1990. Long-term exposure of rats to perchloroethylene, with and without a post-exposure solvent-free recovery period: Effects on brain lipids. Toxicol Lett 52:279-285.
• Levine B, Fierro MF, Goza SW, et al. 1981. A tetrachloroethylene fatality. J Forensic Sci 26:206-209.
• Lukaszewski T. 1979. Acute tetrachloroethylene fatality. Clin Toxicol 15:411-415.
• Pegg DG, Zempel JA, Braun WH, et al. 1979. Disposition of (14C) tetrachloroethylene following oral and inhalation exposure in rats. Toxicol Appl Pharmacol 51:465-474.
• Savolainen H, Pfaffli P, Tengen M, et al. 1977. Biochemical and behavioral effects of inhalation exposure to tetrachloroethylene and dichloromethane. J Neuropathol Exp Neurol 36:941-949.
• Shafer TJ, Bushnell PJ, Benignus VA, et al. 2005. Perturbation of voltage-sensitive Ca2+ channel function by volatile organic solvents. J Pharmacol Exp Ther 315(3):1109-1118.
• Tucker JD, Sorensen KJ, Ruder AM, et al. 2011. Cytogenetic analysis of an exposed-referent study: Perchloroethylene-exposed dry cleaners compared to unexposed laundry workers. Environ Health 10:16.
• WHO. 1987. Tetrachloroethylene health and safety guide. World Health Organization, Distribution and Sales 1211 Geneva 27, Switzerland, 32.
• WHO. 1993. Guidelines for drinking water quality. 2nd ed. World Health Organization, Geneva, Switzerland, 63-64, 175.
• WHO. 2000. Tetrachloroethylene. In: Air Quality Guidelines. Geneva, Switzerland: World Health Organization.
• WHO. 2003. Tetrachloroethene in drinking-water. Background document for development of WHO guidelines for drinking-water quality. Geneva, Switzerland: World Health Organization.
• WHO. 2010. Guidelines for indoor air quality: Selected pollutants. Geneva, Switzerland: World Health Organization.
• WHO. 2011. Guidelines for drinking-water quality. 4th ed. Geneva, Switzerland: World Health Organization.
• Arrêté du 5 décembre 2012, Journal officiel du 09 décembre 2012, relatif aux prescriptions générales applicables aux installations classées pour la protection de l'environnement soumises à déclaration sous la rubrique n° 2345 relative à l'utilisation de solvants pour le nettoyage à sec et le traitement des textiles ou des vêtements.

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Microbiology

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Enzyme

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Binding

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Indigo

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Model