Skip to main content
Journal of Preventive Medicine and Hygiene logoLink to Journal of Preventive Medicine and Hygiene
. 2019 Mar 29;60(1):E50–E57. doi: 10.15167/2421-4248/jpmh2019.60.1.1080

Skin safety and health prevention: an overview of chemicals in cosmetic products

A PANICO 1, F SERIO 1, F BAGORDO 1, T GRASSI 1,, A IDOLO 1, M DE GIORGI 1, M GUIDO 1,2, M CONGEDO 3, A DE DONNO 1,2
PMCID: PMC6477564  PMID: 31041411

Summary

Introduction

Cosmetic products contain a wide range of chemicals to which we are exposed every day. The aim of the study was to determine the presence of potential dangerous substances which can cause adverse health effects by examining product labels.

Materials and methods

A total of 283 products were collected from various shops in Lecce (Italy) and divided into 3 categories: rinse-off, leave-on and make-up. The label of every product was examined and a list including fragrances, preservatives and other chemicals of concern was created.

Results

Fragrances were present in 52.3% of the examined products, mostly limonene (76.9%) and linalool (64.6%) but also citronellol (34.1%), geraniol (31.5%), coumarin (30%) and hexyl cinnamal (29.2%). Preservatives showed a rate of 60% and the most frequently identified were phenoxyethanol (48.7%), sodium benzoate (35.6%), potassium sorbate (22%), methylparaben (15.2%) and MI/MCI (9.9%). The other chemicals of concern were detected in 58% of products; included PEGs (62.3%), acrylate copolymer (34%), petrolatum (17.2%), polysorbates (14,8%), BHT (14.7%), ethylhextyl methoxycinnamate (13.6%), benzophenone-1 (3.7%), benzophenone-3 (4.9%), BHA (1.6%), cocamide DEA and toluene (1.2%).

Conclusions

The use of many of these substances is allowed within certain limits, due to their toxicity at higher concentrations. Other important aspects should be considered as, for instance, the possibility of long-term effects. On the other hand, other substances may induce several acute adverse side-effects, i.e. contact dermatitis and allergic reactions. For these reasons, an enhancement of the criteria used for cosmetics formulation is required since many chemicals used singularly or combined are potentially unsafe.

Key words: Health Prevention, Cosmetics, Cocktail Effect, Additive Effect

Introduction

In their everyday life people are exposed to a great range of chemicals most of which occur naturally in the environment, but others are derived from human activities, being present in foods, water and various daily use products.

Because our skin is the largest surface of the body interacting with external environment, it is both involuntarily exposed to abiotic [1, 2] and biotic factors [3, 4], and voluntarily, due to personal care and cosmetic products use. Many of these are used or applied on a daily basis and in different ways, consequently, these products are assumed for enhancing our personal hygiene and appearance and they are reputed to be harmless for body’s health.

In the light of the frequent and intimate nature of the contact on skin and mucosa with these products, it is important that they do not contain potentially dangerous substances.

As a matter of fact, all the ingredients used in cosmetic products meet certain regulatory requirements [5]. However, the use of many substances is allowed within certain limits, due to their toxicity at higher concentrations. Other important aspects should be considered as, for instance, the possibility of long-term effects [6, 7]. On the other hand, other substances may induce several acute adverse side-effects, i.e. contact dermatitis and allergic reactions [8]. Moreover, the everyday use and continuous exposition of humans to a wide range of personal care products and to different kinds of chemicals, derived from several sources, may cause the so-called “cocktail effect” due to the synergistic interaction of different substances and, also, the “additive effect” because of the presence of the same ingredient in many products [9, 10].

The purpose of the current study was to determine, among the ingredients listed on the label, the presence of substances with known adverse health effects in commonly used personal care and cosmetic products. We considered fragrances, preservatives and other substances known as skin sensitizers or potentially harmful on general health.

Materials and methods

Different kinds of beauty and hygiene products were selected between October and November 2017 from various shops in Lecce (Italy), mainly supermarkets with nationwide coverage, beauty shops, and pharmacies as well as online shops. Ingredient information from labels was collected by taking photos in the shops or downloading data sheets from webshops. Because of the lack of available data on sales rates of specific products to the public, as in other studies [11], a crude selection of products estimated to be sold in large volume was made, on the basis of information from shop assistants and the authors’ own perceptions.

All products were divided into 3 categories: rinse-off products (shower gel, shampoo, toothpaste, liquid soap, intimate soap, shaving foam) leave-on products (body cream, face cream, hand cream, deodorant, sunscreen, aftershave) and make-up ones (lipstick, lipbalm, foundation, nail polish). Such a classification was based on the time of skin application: rinse-off products stay a very short time on it, as they are usually rapidly washed away (even if it would also be appropriate to consider the frequency of application); leave-on and make-up products stay longer on the skin, but the former are more usually used for skin care, in order to protect it, perfume it and keep it in good conditions (moisturising, nourishing, tonifying, etc.), the latter have an aesthetic purpose and are intended to improve someone’s look.

Every group included also organic and children’s products. The first were identified on the basis of organic and natural certifications disclosed on the brand’s website and indicated on the label (Cosmos, Ecolabel UE, Ecocert, Icea, Natrue, etc.); the latter showed on the label the word “baby” or “kids”.

Subsequently, the label of every product was examined and chemicals which could possibly affect human health were detected. The selection of substances was based on scientific evidence: for fragrances the list of 26 allergens which have been identified as skin sensitizer by the Scientific Committee on Consumer Safety (SCCS) and whose names should be listed on the label [12] was considered; for the other substances a literature’s review was conducted [13-15] and only those reporting possible harmful effects on human heath were selected.

A list with fragrances, preservatives and other chemicals of concern, including some UV filters, antioxidants, emulsifiers, surfactants and other synthetic compounds, was created. Data were recorded in Microsoft® Excel and analysed by calculating rate, median and maximum of substances for every category. No chemical analyses were performed in the present study.

Results

A total of 283 products were examined: 112 rinse-off, 103 leave-on and 68 make-up (Tab. I). Fragrances individuated on the labels were 19, preservatives were 16 and other chemicals of concern were 11.

Tab. I.

Products divided into rinse-off, leave-on and make-up categories with frequency of occurrence and proportion of products containing fragrances, preservatives and other chemicals of concern and their distribution in term of median and maximum.

Examined products Products containing fragrances Products containing preservatives Products containing other chemicals of concern
N (%) Median Max N (%) Median Max N (%) Median Max
Rinse-off 112 69 (61.6) 2 10 84(75) 2 6 65(58) 2 5
Leave-on 103 61 (59.2) 6 15 64 (62.1) 2 7 55 (53.4) 2 7
Make-up 68 18 (26.5) 2.5 6 22 (32.4) 2 7 44 (64.7) 2 5
Total 283 148 (52.3) 3 15 170(60) 2 7 164(58) 2 7

FRAGRANCES

The 19 fragrances individuated (Tab. II) are all included in the list of 26 allergens redacted by SCCS, whereas the missing seven ones were: amylcinnamyl alcohol, anise alcohol, benzyl cinnamate, cinnamal, evernia furfuracea, evernia prunastri, methyl 2-octynoate. More than fifty-two per cent of the products contained at least one of the fragrances investigated, especially rinse-off products (61.6%). Generally, the most frequently identified fragrances were limonene (76.9%), linalool (64.6%), citronellol (34.1%), geraniol (31.5%), coumarin (30%) and hexyl cinnamal (29.2%). Moreover, limonene was more present in rinse-off (70.7%) and make-up products (73.3%), whereas linalool was more found in leave-on ones (87.7%).

Tab. II.

Frequency of occurrence and percentage of fragrances identified on the label of selected products and referring to rinse-off, leave-on and make-up categories.

Fragrances CAS no. Rinse-off Leave-on Make-up Total
(n) (%) (n) (%) (n) (%) (n) (%)
Alpha-isomethyl ionone 127-51-5 6 10.3 22 38.6 4 26.7 32 24.2
Amyl cinnamal 122-40-7 3 3.2 3 5.3 1 6.7 7 5.4
Benzyl alcohol 100-51-6 25 29.4 25 32.5 5 17.2 55 28.8
Benzyl benzoate 120-51-4 3 3.2 9 15.8 4 26.7 16 12.1
Benzyl salicylate 118-58-1 12 20.7 20 35.1 1 6.7 33 25.4
Butylphenyl methylpropional 80-54-6 12 20.7 16 28.1 - - 28 21.5
Cinnamyl alcohol 104-54-1 1 1.7 3 5.3 - - 4 3.1
Citral 5392-40-5 2 3.4 26 45.6 4 26.7 32 24.2
Citronellol 106-22-9 11 19 33 56.9 1 6.7 45 34.1
Coumarin 91-64-5 11 19 26 45.6 2 13.3 39 30
Eugenol 97-53-0 10 17.2 11 19.3 1 6.7 22 16.9
Farnesol 4602-84-0 - - 3 5.3 - - 3 2.3
Geraniol 106-24-1 7 12.1 32 56.1 2 13.3 41 31.5
Hexyl cinnamal 101-86-0 18 31 18 31.6 2 13.3 38 29.2
Hydroxycitronellal 107-75-5 2 3.4 8 14 1 6.7 11 8.5
Hydroxyisohexyl 3-cyclohexene carboxaldehyde 31906-04-4 - - 12 21.1 - - 12 9.2
Isoeugenol 97-54-1 - - 6 10, 5 - - 6 4.4
Limonene 138-86-3 41 70.7 48 84.2 11 73.3 100 76.9
Linalool 78-70-6 26 44.8 50 87.7 8 53.3 84 64.6

In addition, the presence of fragrances was found in organic and children’s products (Tab. III), respectively 56.3% and 18.6%. Limonene was the fragrance most listed on the labels for both kinds of products (respectively 84.4 and 83.3%), followed by linalool (65.6 and 33.3%) (Not in the table).

Tab. III.

Frequency of occurrence and percentage of substances identified on the label of children’s products.

Substances Products n %
Limonene Shower gel, toothpaste, sunscreen, lipstick, lipbalm 16 83.3
Linalool Toothpaste, sunscreen, lipstick, lipbalm 7 33.3
Citral Lipbalm 1 5
Benzyl alcohol Shower gel, sunscreen, nail polish 5 25
Eugenol Toothpaste 1 5
Alpha-isomethyl ionone Sunscreen 1 5
Citronellol Sunscreen 1 5
Coumarin Sunscreen 1 5
Potassium sorbate Shower gel, intimate soap, toothpaste, liquid soap 4 12.5
Sodium benzoate Shower gel, shampoo, intimate soap, toothpaste, liquid soap, body cream 12 37.5
Phenoxyethanol Shower gel, shampoo, toothpaste, body cream, sunscreen, lipstick, nail polish 14 43.8
Chlorphenesin Shampoo, body cream 2 6.3
Imidazolidinyl urea Shampoo 1 3.1
Diazolidinyl Urea Nail polish 1 3.1
Methylparaben Lipstick 1 3.1
Propylparaben Lipstick 1 3.1
Benzoic acid Sunscreen 1 3.1
Cocamide DEA Shampoo 1 4
BHA Shampoo 1 4
BHT Shower gel, shampoo, lipbalm 4 16
PEG’s Shower gel, shampoo, intimate soap, toothpaste, liquid soap, body cream, sunscreen 17 68
MI/MCI Shampoo, liquid soap 2 8
Ethylhextyl methoxycinnamate Lipbalm 3 12
Petrolatum Body cream, lipstick, lipbalm 6 24
Acrylate copolymer Shampoo, sunscreen, lipstick, nail polish 6 24
Polysorbate-80/-60/-20 Shampoo, body cream 3 12

PRESERVATIVES

Sixty per cent of the selected products contained at least one of the preservatives investigated, above all among rinse-off products (75%). The most frequently identified preservatives (Tab. IV) were phenoxyethanol (48.7%), sodium benzoate (35.6%), potassium sorbate (22%), methylparaben (15.2%) and methylisothiazolinone/methylchloroisothiazolinone (MI/MCI) (9.9%). Sodium benzoate was the most common preservative in rinse-off products (57.6%) and phenoxyethanol in leave-on (70.1%) and make-up ones (58.6%).

Tab. IV.

Frequency of occurrence and percentage of preservatives identified on the label of selected products and referring to rinse-off, leave-on and make-up categories.

Preservatives CAS no. Rinse-off Leave-on Make-up Total
(n) (%) (n) (%) (n) (%) (n) (%)
Methylparaben 99-76-3 8 9.4 16 20.8 5 17.2 29 15.2
Ethylparaben 120-47-8 2 2.4 11 14.3 3 10.3 16 8.4
Propylparaben 94-13-3 3 3.5 8 10.4 4 13.8 15 7.9
Butylparaben 94-26-8 - - 4 5.2 2 6.9 6 3.1
Triclosan 3380-34-5 4 4.7 2 2.6 - - 6 3.1
Imidazolidinyl Urea 39236-46-9 2 2.4 8 10.4 1 3.4 11 5.8
Diazolidinyl Urea 7849-02-8 - - - - 1 3.4 1 0.5
5-bromo-5-nitro-1, 3 dioxane 30007-47-7 1 1.2 - - - - 1 0.5
2-bromo-2-nitropropane-1, 3-diol 52-51-7 1 1.2 - - - - 1 0.5
DMDM Hydantoin 6440-58-0 12 14.1 4 5.2 - - 16 8.4
Phenoxyethanol 122-99-6 22 25.9 54 70.1 17 58.6 93 48.7
Methylisothiazolinone/ Methylchloroisothiazolinone 2682-20-4, 26172-55-4, 55965-84-9 19 22.4 - - - - 19 9.9
Chlorphenesin 104-29-0 1 1.2 2 2.6 2 6.9 5 2.6
Benzoic acid 65-85-0 5 5.9 9 11.7 1 3.4 15 7.9
Sodium benzoate 1-23-235 49 57.6 17 22.1 2 6.9 68 35.6
Potassium sorbate 24634-61-5 23 27.1 15 19.5 4 13.8 42 22

Four different parabens were identified (methylparaben, ethylparaben, propylparaben, butylparaben) and almost 15% of the products contained one or more parabens, mostly leave-on products (face and hand cream, sunscreen, aftershave). The most detected was methylparaben, found in all of those products containing at least one paraben, followed by ethylparaben (55.2%) and propylparaben (51.7%). All four parabens were contained in six products (foundation, face cream, lipstick, aftershave, two sunscreens) and three parabens in three products (aftershave, two face creams).

Formaldehyde-releasers (imidazolidinyl urea, diazolidinyl urea, 5-bromo-5-nitro-1, 3 dioxane, 2-bromo-2-nitropropane-1, 3-diol, DMDM hydantoin) showed almost the same rate of parabens (15%) but they were more present in rinse-off products. Among the five formaldehyde-releasers, the most common were DMDM hydantoin (53.6%) and imidazolidinyl urea (39.3%), which were both found also in two body lotions.

MI/MCI was found in 9.9% of the examined products, especially in rinse-off ones. Six products contained triclosan (3.1%) (two deodorants, two intimate soaps, a liquid soap, a shaving foam).

As far as children’s products are concerned, more than seventy-two per cent contained at least one of the preservatives among those considered, in particular the most present was phenoxyethanol (43.8%), followed by sodium benzoate (37.5%). Formaldehyde-releasers were found into two products (shampoo, nail polish), parabens in a lipstick, chlorphenesin in a body cream and a shampoo, MI/MCI in two rinse-off products (shampoo, liquid soap) (Tab. III).

Almost fifty-four per cent of organic products showed on the label at least one of the preservatives investigated, in particular the most common was sodium benzoate (50%) followed by potassium sorbate (47.2%). It is notable the presence of triclosan in an organic deodorant.

OTHER CHEMICALS OF CONCERN

Fifty-eight per cent of the examined products contained at least one of the other chemicals of concern, especially make-up ones (64.7%). The substances most frequently identified in this group (Tab. V) were PEGs (polyethylene glycols) (62.3%) and acrylate copolymer (34%). The first were more common in rinse-off (81.5%) and leave-on products (69.1%), while make-up ones showed a high presence of acrylates (45.2%) and petrolatum (33.3%).

Tab. V.

Frequency of occurrence and percentage of other chemicals of concern identified on the label of selected products and referring to rinse-off, leave-on and make-up categories.

Other chemicals CAS no. Rinse-off Leave-on Make-up Total
(n) (%) (n) (%) (n) (%) (n) (%)
PEGs* 25322-68-3 53 81.5 38 69.1 10 23.8 101 62.3
Acrylate copolymer 25133-97-5 16 24.6 20 36.4 19 45.2 55 34
Petrolatum 8009-03-8 2 3.1 12 21.8 14 33.3 28 17.2
Polysorbate-80/-60/-20 9005-65-6, 9005-67-8, 9005-64-5 16 24.6 7 12.7 1 2.4 24 14.8
Ethylhextyl methoxycinnamate 5466-77-3 - - 9 16.4 13 31 22 13.6
BHA 25013-16-5 1 1.2 - - 2 6.9 3 1.6
BHT 128-37-0 3 3.5 14 18.2 11 37.9 28 4.7
Benzophenone-1 131-56-6 - - - - 6 14.3 6 3.7
Benzophenone-3 131-57-7 - - 3 5.5 5 11.9 8 4.9
Cocamide DEA 68603-42-9 2 3.1 - - - - 2 1.2
Toluene 108-88-3 - - - - 2 4.8 2 1.2

*we considered all ingredients indicated on labels as “PEG” or “-eth”, followed by a number.

UV filters (ethylhextyl methoxycinnamate, benzophenone-1, benzophenone-3) were present in 19.1% of the products, especially in make-up ones (45.2%). BHT showed a rate of 14.7% and was found with BHA (butylated hydroxyanisole) in three products (a shampoo, two lipbalms). Noteworthy, two nail polishes which contained toluene.

Referring to children’s products, almost fifty-eight per cent contained one or more of the aforementioned substances. Most of these (68%) showed PEGs on their label and the presence of ethylhextyl methoxycinnamate in three lipbalms is remarkable (Tab. III). Organic products contained this type of compounds for a rate of 10.9% and a nail polish contained benzophenone-3.

Discussion

In this study the presence of chemicals that can affect human health in consumer-available personal care and cosmetic products used by a large part of the population and frequently into contact with the body was examined.

More attention should be given to leave-on and make-up products which stay longer on the skin. For this reason, dangerous substances could determine greater negative effects on human’s health. Make-up products, in particular, are often applied close to mucosa and frequently used by more sensitive categories, such as teenagers.

Fragranced ingredients are widespread diffused in cosmetic products but many of these may cause sensitizations, allergies and skin irritations [11]. For this reason, the EU established limits to their utilization and the obligation to indicate their presence on products labels, when the concentration is higher than 0.01% in rinse-off products, and 0.001% in leave on products [5].

The most common fragrance identified in the present study was limonene (76.9%) which, together with citral (24.2%), is classified as skin sensitizers (H317), according to the regulation on the classification, labelling and packaging of substances and mixtures (CLP) [16]. In addition, many fragrance ingredients were categorized as weak allergens [17]; since a large number of products contains a mixture of fragrances, the consumers are more likely to be exposed to mixtures of allergens. Bonefeld et al. [18] found that mixtures of fragrance allergens have an increased potency in sensitization and elicitation of contact allergy as compared with an isolated fragrance allergen.

Among preservatives, parabens are considered as a class of endocrine disruptors, especially propylparaben and butylparaben. Many studies observed that parabens were able to chemically imitate the oestrogenic activity leading to adverse health outcomes [19, 20]. Moreover, parabens could play a role in the development of human breast, ovary and testicles cancer [21, 22]. For these reasons, many countries have banned the use of some parabens in personal care products intended for newborns and children [23].

Formaldehyde-releasers are important sources of formaldehyde exposure and allergic Contact Dermatitis They are able to release formaldehyde that has the capability to cause hypersensitivity reactions [24]. For some time now, formaldehyde is considered carcinogenic to humans [25] and, even if concentrations of these kinds of preservatives added to cosmetics are very low, they are still present in a large number of products whose use occurs frequently and daily.

MCI and MI are preservatives whose use has recently increased in cosmetics, but there is a limit of concentration both for the single ingredient and for the MI/MCI mixture [5]. Many studies focused on contact allergies associated with the use of MI/MCI, even if the dose allowed is respected [26, 27]. The use of chlorphenesin is allowed in concentration lower than 0.3% [28]. At a higher concentration it may cause irritations and contact dermatitis, especially on sensitive skin [29]. Due to the possibility of collateral side-effects on children, in particular on the respiratory tract and the central nervous system, the Food and Drug Administration (FDA) advised against the use of products containing chlorphenesin for children and women while breastfeeding [30]. In this work we underlined the presence of clorphenesin in two children’s products.

We found triclosan in few products, however, because of its relevance, it is important to focus attention on it. It is an antimicrobial additive considered potentially harmful for health as an endocrine disruptor, as a result of a prolonged use [31-33]. It may be found together with dioxin, formed during its synthesis process, which could also be formed by photodegradation of triclosan in the urban wastewater [34]. Moreover, the massive diffusion of this antimicrobial compound may determine an increase in the bacterial resistance to the most common antibiotics used in the medical field [35]. The widespread use of this substance is demonstrated by the detection of triclosan traces in fish’s fatty tissues and, even worse, in maternal milk. That evidence confirms the continuous exposition to very low or minimal concentrations of triclosan may lead to living organisms to absorb that compound [36, 37]. For all these reasons, triclosan was banned in 2013 by the FDA [38]. Nevertheless, in Europe the use of triclosan is still allowed in cosmetic products.

Lastly other chemicals, considered in our investigation, were substances different from fragrances and preservatives. Benzophenone-1 and benzophenone-3 are chemical filters used for the protection from UV radiations, reputed endocrine disruptors. Exposure to these ingredients, although definitive studies are lacking, could cause negative effects on humans, as well as a neuronal delay and alterations in behavioural development, congenital malformations, fertility deficiency for men, etc. [39, 40]. In addition, the International Agency for Research on Cancer (IARC) classified benzophenone as a possibly carcinogenic to humans (2B group) [41]. These ingredients have good lipophilic properties and after only a few hours from their application on the skin, it is possible to detect them in biological fluids like maternal milk [42]. Also ethylhexyl methoxycinnamate is a UV filter added to cosmetics, and some studies show how it can affect and modify the regulation of the endocrine system [43].

Considering BHA and BHT, the Cosmetic Ingredient Review (CIR) Expert Panel established concentration limits for these substances (0.5% max) because of their uncertain toxicological profile and the potential irritating power on skin and mucosa [44, 45].

Cocamide DEA is a skin irritant [46], classified in 2B group by the IARC [47]. Moreover, in 2012 the California Office of Environmental Health Hazard Assessment added cocamide DEA to the list of chemical compounds that cause cancer [48].

PEGs are characterised by low cutaneous toxicity and generally they are weakly irritants. They come from the polymerization of ethylene oxide, a well-known carcinogenic agent [49]. These substances can contain residual impurities derived from the ethoxylation process: ethylene oxide, dioxane, polycyclic aromatic compounds, heavy metals like lead, iron, cobalt, nickel, cadmium, arsenic [50].

Petrolatum (indicated on labels as paraffinum liquidum/petrolatum/paraffin/vaseline/mineral oil) is widely used in cosmetics but there are some potential health risks linked to its utilization, especially for the possible presence of impurities. In 2011 a scientific study showed that hydrocarbons derived from petrolatum are the most present contaminants in human body and the contamination occurs, above all, through the inhalation of polluted air, the ingestion of contaminated food and cutaneous absorption. This study also underlined that cosmetics can represent one of the most significant source of these compounds [51].

Toluene exposure from nail polish application was assumed to occur through both dermal and inhalation routes: a high concentration can cause irritation on the mucosa and skin irritation. It was listed in 1991 under State of California Proposition 65, as a chemical known for causing reproductive toxicity and having adverse effects on the central nervous system [52].

Finally, acrylates and polysorbates are considered weakly irritants: the concern related to the first compounds is the possible presence of toxic residuals like acrylic and methacrylic acid which are characterized by allergenic activity [53]; while the second ones are less irritants, even if cases of contact dermatitis due to these substances have been proved [54].

Conclusions

As a result of what explained, it is evident how, through the use of cosmetics, most people are exposed worldwide to a variety of potentially harmful substances.

Although the amounts may be small, and their effects sometimes poorly understood, continuous exposure to a mix of these chemicals over long periods could have consequences for the health and well-being of people and society. Actually, the current legislation takes these risks into account and many substances are subject to a threshold concentration, but there is a potential “cocktail effect” due to the utilization of combined products during the daytime. In addition, the same substance can be found in more than one product and can derive from different sources (“additive effect”), in this way, the safety threshold established could be overcome. For example, we can think about formaldehyde which is found in a variety of consumer products: clothing, plastics, dry cleaning agents, paper, glue, drywall board, resins, wood panelling, etc.

It is necessary to improve the legislative approach, since there are chemicals whose use is not completely safe, but still allowed, so that it would be suitable to resort to the precautionary principle. Moreover, it would be appropriate to enhance cytotoxicity studies in order to assess the actual harmlessness of the formulations in vitro [55] and to prefer alternative substances [56] compared to those potentially dangerous used for the stability and the attractiveness of the products.

Acknowledgements

The authors gratefully thank Gianfranco Calogiuri for critical revisions of the manuscript.

Footnotes

Funding sources: this research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

Conflict of interest statement

None declared.

Authors’ contributions

All authors made substantial contributions to the conception and design of the study and were involved in drafting and critically revising the manuscript in terms of intellectual content. In addition, AP conceived the study, performed the analysis and interpreted the results. FS contributed in the interpretation of results. FB contributed in the analysis and interpretation of data. TG was involved in the study design and methodology. AI and MDG were involved in collection and management of data. MG and MC were involved in planning and supervising the work. ADD was involved in study design, interpretation of results and supervised the findings of this work.

References

  • [1].Anveden Berglind I, Meding B, Alderling M. Life-style factors and hand eczema: a population-based study. Contact Dermatitis 2010;63(suppl.1):11-38. 2 doi: 10.1186/1471-5945-13-14. [Google Scholar]
  • [2].Sasaya H, Oiso N, Kawara S, Kawada A. Airborne contact dermatitis from cigarettes. Contact Dermatitis 2007;56:173-4. doi: 10.1111/j.1600-0536.2007.01041.x. [DOI] [PubMed] [Google Scholar]
  • [3].Aalto-Korte K. Lichen contact allergy. Contact Dermatitis 2010;63(suppl.1):11-38. doi: 10.4103/0019-5154.91832. [DOI] [PubMed] [Google Scholar]
  • [4].De Donno A, Idolo A, Bagordo F. Epidemiology of jellyfish stings reported to summer health centres in the Salento peninsula (Italy). Contact Dermatitis 2009;60:330-5. doi: 10.1111/j.1600-0536.2009.01561.x. [DOI] [PubMed] [Google Scholar]
  • [5].Regulation (EC) no. 1223/2009 of the European Parliament and of the council of 30 November 2009 on cosmetic products. Official Journal of the European Union. [Google Scholar]
  • [6].Patisaul HB, Adewale HB. Long-term effects of environmental endocrine disruptors on reproductive physiology and behaviour. Front Behav Neurosci 2009;3(10):1-18. doi: 10.3389/neuro.08.010.2009. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [7].Park JD, Zheng W. Human Exposure and health effects of inorganic and elemental mercury. J Prev Med Public Health 2012;45(6):344-52. doi: 10.3961/jpmph.2012.45.6.344. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [8].Duarte I, Lage ACC. Frequency of dermatoses associated with cosmetics. Contact Dermatitis 2007;56:211-3. doi: 10.1111/j.1600-0536.2006.01051.x. [DOI] [PubMed] [Google Scholar]
  • [9].Kartono F, Mailbach HI. Irritants in combination with a synergistic or additive effect on the skin response: an overview of tandem irritation studies. Contact Dermatitis 2006;54:303-312. doi: 10.1111/j.0105-1873.2006.00792.x. [DOI] [PubMed] [Google Scholar]
  • [10].Uter W, Yazar K, Kratz EM, Mildau G, Lidén C. Coupled exposure to ingredients of cosmetic products: I. Fragrances. Contact Dermatitis 2013;69:335-41. doi: 10.1111/cod.12245. [DOI] [PubMed] [Google Scholar]
  • [11].Yazar K, Johnsson S, Lind ML, Boman A, Lidén C. Preservatives and fragrances in selected consumer-available cosmetics and detergents. Contact Dermatitis 2010;64(5):265-72. doi: 10.1111/j.1600-0536.2010.01828.x. [DOI] [PubMed] [Google Scholar]
  • [12].Scientific Committee on Consumer Safety (SCCS). Opinion on fragrance allergens in cosmetic products. SCCS/1459/11. The SCCS adopted this opinion at its 15th plenary meeting of 26-27 June 2012. [Google Scholar]
  • [13].Pastor-Nieto MA, Alcántara-Nicolás F, Melgar-Molero V, Pérez-Mesonero R, Vergara-Sánchez A, Martín-Fuentes A, González-Muñoz P, de Eusebio-Murillo E. Preservatives in personal hygiene and cosmetic products, topical medications, and household cleaners in Spain. Actas Dermosifiliogr 2017;108:758-70. doi: 10.1016/j.ad.2017.04.003. [DOI] [PubMed] [Google Scholar]
  • [14].In SJ, Kim SH, Go RE, Hwang KA, Choi KC. Benzophenone-1 and Nonylphenol Stimulated MCF-7 breast cancer growth by regulating cell cycle and metastasis-related genes via an estrogen receptor α-dependent pathway. J Toxicol Environ Health A 2015;78(8):492-505. doi: 10.1080/15287394.2015.1010464. [DOI] [PubMed] [Google Scholar]
  • [15].Lim SK, Shin HS, Yoon KS, Kwack SJ, Um YM, Hyeon JH, Kwack HM, Kim JY, Kim TY, Kim YJ, Roh TH, Lim DS, Shin MK, Choi SM, Kim HS, Lee BM. Risk assessment of volatile organic compounds Benzene, Toluene, Ethylbenzene, and Xylene (BTEX) in consumer products. J Toxicol Environ Health A 2014;77:22-4. doi: 10.1080/15287394.2014.955905. [DOI] [PubMed] [Google Scholar]
  • [16].Regulation (EC) no. 1272/2008 of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures, amending and repealing Directives 67/548/EEC and 1999/45/EC, and amending Regulation (EC) no. 1907/2006. Official Journal of the European Union. [Google Scholar]
  • [17].Basketter D, Kimber I. Predictive tests for irritants and allergens and their use in quantitative risk assessment. In: Contact Dermatitis, ed. Johansen JD, Frosch PF, Lepoitte-vin J-P. (eds). Berlin: Springer; 2011. pp. 229-240. [Google Scholar]
  • [18].Bonefeld CM, Nielsen MM, Rubin IMC, Torp Vennegaard M, Dabelsteen S, Gimenéz-Arnau E, Lepoittevin JP, Geisler C, Johansen JD. Enhanced sensitization and elicitation responses caused by mixtures of common fragrance allergens. Contact Dermatitis 2011;65:336-42. doi: 10.1111/j.1600-0536.2011.01945.x. [DOI] [PubMed] [Google Scholar]
  • [19].Howdeshell KL, Hotchkiss AK, Gray LE., Jr Cumulative effects of antiandrogenic chemical mixtures and their relevance to human health risk assessment. Int J Hyg Environ Health 2016;220(2 pt A):179-88. doi: 10.1016/j.ijheh.2016.11.007. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [20].Orton F, Ermler S, Kugathas S, Rosivatz E, Scholze M, Kortenkamp A. Mixture effects at very low doses with combinations of anti-androgenic pesticides, antioxidants, industrial pollutant and chemicals used in personal care products. Toxicol Appl Pharmacol 2014;278(3):201-8. doi: 10.1016/j.taap.2013.09.008. [DOI] [PubMed] [Google Scholar]
  • [21].Darbre PD, Harvey PW. Paraben esters: review of recent studies of endocrine toxicity, absorption, esterase and human exposure, and discussion of potential human health risks. J Appl Toxicol 2008;28(5):561-78. doi: 10.1002/jat.1358. [DOI] [PubMed] [Google Scholar]
  • [22].Giulivo M, Lopez de Alda M, Capri E, Barceló D. Human exposure to endocrine disrupting compounds: their role in reproductive systems, metabolic syndrome and breast cancer. A review. Environ Res 2016;151:251-264. doi: 10.1016/j.envres.2016.07.011. [DOI] [PubMed] [Google Scholar]
  • [23].Commission Regulation (EU) no. 1004/2014 of 18 September 2014 amending Annex V to Regulation (EC) no. 1223/2009 of the European Parliament and of the Council on cosmetic products. Official Journal of the European Union. [Google Scholar]
  • [24].De Groot AC, White IR, Flyvholm M, Lensen G, Coenraads P. Formaldehyde-releasers in cosmetics: relationship to formaldehyde contact allergy. Part 1. Characterization, frequency and relevance of sensitization, and frequency of use in cosmetics. Contact Dermatitis 2010;62(1):2-17. doi: 10.1111/j.1600-0536.2009.01615.x. [DOI] [PubMed] [Google Scholar]
  • [25].International Agency for Research on Cancer (IARC). Formaldehyde, 2-butoxyethanol and 1-tert-butoxypropan-2-ol. IARC monographs on the evaluation of carcinogenic risks to humans. WHO, IARC Press, Lyon, France: 2006;88:1-478. [PMC free article] [PubMed] [Google Scholar]
  • [26].Lundov MD, Krongaard T, Menné TL, Johansen JD. Methylisothiazolinone contact allergy: a review. Br J Dermatol 2011;165(6):1178-82. doi: 10.1111/j.1365-2133.2011.10523.x. [DOI] [PubMed] [Google Scholar]
  • [27].Pónyai G, Németh I, Temesvári E. Methylchloroisothiazolinone/methylisothiazolinone and methylisothiazolinone sensitivity in Hungary. Dermatol Res Pract 2016;4579071 doi: 10.1155/2016/4579071. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [28].European Union. Consolidated version of Cosmetic Directive 76/768/EEC, as amended, Annexes I through IX, 2010. Available at: http://ec.europa.eu/enterprise/sectors/cosmetics/documents/directive/#h2-technical-adaptations-to-be-incorporated-in-the-consolidated-text Accessed on 10/04/2018.
  • [29].Dyring-Andersen B, Elberling J, Duus Johansen J, Zachariae C. Contact allergy to chlorphenesin. JEADV 2015;29(5):1019 doi: 10.1111/jdv.12437. [DOI] [PubMed] [Google Scholar]
  • [30].Food and Drug Administration (FDA). U.S. FDA Warns consumers against using mommy’s bliss nipple cream product can be harmful to nursing infants, 2008. Available at: https://www.sfda.gov.sa/en/drug/news/pages/332-ar-01-6.aspx Accessed on 20/04/2018.
  • [31].Rodríguez PEA, Sanchez MS. Maternal Exposure to Triclosan Impairs Thyroid Homeostasis and Female Pubertal Development in Wistar Rat Offspring. J Toxicol Environ Health A 2010;73(24):1678-88. doi: 10.1080/15287394.2010.516241. [DOI] [PubMed] [Google Scholar]
  • [32].Jung EM, An BS, Choi KC, Jeung EB. Potential estrogenic activity of triclosan in the uterus of immature rats and rat pituitary GH3 cells. Toxicol Lett 2012;208:142-8. doi: 10.1016/j.toxlet.2011.10.017. [DOI] [PubMed] [Google Scholar]
  • [33].Huang H, Du G, Zhang W, Hu J, Wu DI, Song L, Xia Y, Wang X. The in vitro estrogenic activities of triclosan and triclocarban. J Appl Toxicol 2014;34(9):1060-7. doi: 10.1002/jat.3012. [DOI] [PubMed] [Google Scholar]
  • [34].Son HS, Ko G, Zoh KD. Kinetics and mechanism of photolysis and TiO2 photocatalysis of triclosan. J Hazard Mater 2009;166:954-960. doi: 10.1016/j.jhazmat.2008.11.107. [DOI] [PubMed] [Google Scholar]
  • [35].Drury B, Scott J, Rosi-Marshall EJ, Kelly JJ. Triclosan exposure increases triclosan resistance and influences taxonomic composition of benthic bacterial communities. Environ Sci Technol 2013;47(15):8923-30. doi: 10.1021/es401919k. [DOI] [PubMed] [Google Scholar]
  • [36].Olaniyan LW, Mkwetshana N, Okoh AI. Triclosan in water, implications for human and environmental health. Springerplus 2016;5(1):1639 doi: 10.1186/s40064-016-3287-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [37].Allmyr M, Adolfsson-Erici M, McLachlan MS, Sandborgh-Englund G. Triclosan in plasma and milk from Swedish nursing mothers and their exposure via personal care products. Sci Total Environ 2006;372:87-93 doi: 10.1016/j.scitotenv.2006.08.007. [DOI] [PubMed] [Google Scholar]
  • [38].Food and Drug Administration (FDA). Safety and effectiveness of consumer antiseptics; topical antimicrobial drug products for over-the-counter human use; proposed amendment of the tentative final monograph; reopening of administrative record. Federal Register. 2013;78 FR 76443-78. [Google Scholar]
  • [39].Kerdivel G, Le Guevel R, Habauzit D, Brion F, Ait-Aissa S, Pakdel F. Estrogenic potency of benzophenone uv filters in breast cancer cells: proliferative and transcriptional activity substantiated by docking analysis. PLoS ONE 2013;8(4):e60567 doi: 10.1371/journal.pone.0060567. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [40].Schlumpf M, Cotton B, Conscience M, Haller V, Steinmann B, Lichtensteiger W. In vitro and in vivo estrogenicity of UV screens. Environ Health Perspect 2001;109(3):239-44. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • [41].International Agency for Research on Cancer (IARC). Benzophenone. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. WHO, IARC Press, Lyon, France: 2010;101:285-304. [Google Scholar]
  • [42].Schlumpf M, Durrer S, Faass O, Ehnes C, Fuetsch M, Gaille C, Henseler M, Hofkamp L, Maerkel K, Reolon S, Timms B, Tresguerres JA, Lichtensteiger W. Developmental toxicity of UV filters and environmental exposure: a review. Int J Androl 2008;31:144-51. doi: 10.1111/j.1365-2605.2007.00856.x. [DOI] [PubMed] [Google Scholar]
  • [43].Manová E, von Goetz N, Hungerbuhler K. Aggregate consumer exposure to UV filter ethylhexyl methoxycinnamate via personal care products. Environ Int 2015;74:249-57. doi: 10.1016/j.envint.2014.09.008. [DOI] [PubMed] [Google Scholar]
  • [44].Cosmetic Ingredient Review (CIR). 2 Final report on the safety assessment of butylated hydroxyanisole. Int J Toxicol 1984;3(5):83-146. doi: 10.3109/10915818409021273. [Google Scholar]
  • [45].Lanigan RS, Yamarik TA. Final Report on the Safety Assessment of BHT. Int J Toxicol 2002;21(2):19-94. doi: 10.1080/10915810290096513. [DOI] [PubMed] [Google Scholar]
  • [46].Mertens S, Gilissen L, Goossens A. Allergic contact dermatitis caused by cocamide diethanolamine. Contact Dermatitis 2016;75(1):20-4. doi: 10.1111/cod.12580. [DOI] [PubMed] [Google Scholar]
  • [47].International Agency for Research on Cancer (IARC). Some chemicals in industrial and consumer products, some food contaminants and flavourings, and water chlorination by-products. IARC Monographs on the evaluation of carcinogenic risks to humans. WHO, IARC Press, Lyon, France: 2011;101:141-8. [Google Scholar]
  • [48].California’s Office of Environmental Health Hazard Assessment (OEHHA). Benzophenone, Coconut oil diethanolamine condensate (cocamide diethanolamine), diethanolamine and 2-methylimidazole listed effective June 22, 2012 as known to the state to cause cancer. Available at: https://oehha.ca.gov/proposition-65/crnr/benzophenone-coconut-oil-diethanolamine-condensate-cocamide-diethanolamine Accessed on 16/04/2018.
  • [49].International Agency for Research on Cancer (IARC). Ethylene oxide. IARC monographs on the evaluation of carcinogenic risks to humans. A review of human carcinogen: chemical agents and related occupations. WHO, IARC Press, Lyon, France, 2012;100F:379-400. [Google Scholar]
  • [50].Fruijtier-Pölloth C. Safety assessment on polyethylene glycols (PEGs) and their derivatives as used in cosmetic products. Toxicology 2005;214(1-2):1-38. doi: 10.1016/j.tox.2005.06.001. [DOI] [PubMed] [Google Scholar]
  • [51].Concin N, Hofstetter G, Plattner B, Tomovski C, Fiselier K, Gerritzen K, Semsroth S, Zeimet AG, Marth C, Siegl H, Rieger K, Ulmer H, Concin H, Grob K. Evidence for cosmetics as a source of mineral oil contamination in women. J Womens Health (Larchmt) 2011;20(11):1713-9. doi: 10.1089/jwh.2011.2829. [DOI] [PubMed] [Google Scholar]
  • [52].Kopelovich L, Perez AL, Jacobs N, Mendelsohn E, Keenan JJ. Screening-level human health risk assessment of toluene and dibutyl phthalate in nail lacquers. Food Chem Toxicol 2015;81:46-53. doi: 10.1016/j.fct.2015.04.011. [DOI] [PubMed] [Google Scholar]
  • [53].Zaragoza-Ninet V, Blasco Encinas R, Vilata-Corell JJ, Pérez-Ferriols A, Sierra-Talamantes C, Esteve-Martínez A, De La Cuadra-Oyanguren J. Allergic contact dermatitis due to cosmetics: A clinical and epidemiological study in a tertiary hospital. Actas Dermosifiliogr 2016;107(4):329-36. doi: 10.1016/j.ad.2015.12.007. [DOI] [PubMed] [Google Scholar]
  • [54].Palacios Castaño MI, Venturini Díaz M, Lobera Labairu T, González Mahave I, del pozo Gil MD, Blasco Sarramián A. Anaphylaxis due to the excipient polysorbate 80. J Investig Allergol Clin Immunol 2016;26(6):394-6. doi: 10.18176/jiaci.0109. [DOI] [PubMed] [Google Scholar]
  • [55].Serio F, Pizzolante G, Cozzolino G, D’Alba M, Bagordo F, De Giorgi M, Grassi T, Idolo A, Guido M, De Donno A. A new formulation based on ozonated sunflower seed oil: in vitro antibacterial and safety evaluation. Ozone: Science & Engineering. 2017;39(3):139-147. doi: 10.1080/01919512.2016.1272405. [Google Scholar]
  • [56].Papageorgiou S, Varvaresou A, Tsirivas E, Demetzos C. New alternatives to cosmetics preservation. Int J Cosmet Sci 2010;61(2):107-23. doi: 10.1111/j.1468-2494.2010.006093.x. [PubMed] [Google Scholar]

Articles from Journal of Preventive Medicine and Hygiene are provided here courtesy of Pacini Editore

RESOURCES