Click
here to close Hello! We notice that
you are using Internet Explorer, which is not supported by Echinobase
and may cause the site to display incorrectly. We suggest using a
current version of Chrome,
FireFox,
or Safari.
Sci Rep
2017 Aug 10;71:7815. doi: 10.1038/s41598-017-08013-x.
Show Gene links
Show Anatomy links
Sunscreen products impair the early developmental stages of the sea urchin Paracentrotus lividus.
Corinaldesi C
,
Damiani E
,
Marcellini F
,
Falugi C
,
Tiano L
,
Brugè F
,
Danovaro R
.
Abstract
Marine ecosystems are increasingly threatened by the release of personal care products. Among them, sunscreens are causing concern either for the effects on skin protection from UV radiation and for the potential impacts on marine life. Here, we assessed the UVA protective efficacy of three sunscreens on human dermal fibroblasts, including two common products in Europe and USA, and an eco-friendly product. The sunscreens'' effects were also tested on Paracentrotus lividus, a marine species possibly threatened by these contaminants. We found that all tested sunscreens had similar efficacy in protecting human fibroblasts from UVA radiation. Conversely, the sunscreens'' effects on embryo-larval development of P. lividus were dependent on the product tested. In particular, the USA sunscreen, containing benzophenone-3, homosalate and preservatives, caused the strongest impact on the sea urchin development, whereas the eco-friendly sunscreen determined the weakest effects. These results suggest that although the tested products protected human skin cells from UVA-induced damage, they might severely affect the success of recruitment and survival of the sea urchin. Our findings underline the importance of developing eco-friendly sunscreens for minimising or avoiding the impact on marine life while protecting human skin from UV damage.
Figure 1. Viability of human dermal fibroblasts (HDF) and their intracellular levels of ROS after exposure to UVA (275âkJâmâ2). Cell viability, determined by using Guava Via-count dye straight after UVA exposure, time 0 (panel a); cell viability 24âh post-irradiation (panel b); ROS levels determined using carboxy-H2DCFDA probe straight after UVA exposure, time 0 (panel c); ROS levels 24âh post-irradiation (panel d). A, B and C indicate the different sunscreens used to screen HDF. Aâ=âEuropean sunscreen, SPF 50+â; Bâ=âUSA sunscreen, SPF 50; Câ=âEco-friendly sunscreen, SPF 40. PCâ=âpositive control (HDF without sunscreens and exposed to UVA). NCâ=ânegative control (unexposed HDF). Error bars represent standard error (nâ=â5).
Figure 2. Gene expression analysis of MMP1 (panel a) and COL1A1 (panel b) in human dermal fibroblasts (HDF) exposed to UVA (366âkJâmâ2), assessed using qPCR 24âh post-irradiation. Data are reported as normalized fold expression using the 2âââCt method. HDF were screened with sunscreens A (European sunscreen), B (USA sunscreen), C (eco-friendly sunscreen) or with no sunscreen (PCâ=âpositive control) and exposed to UVA. NCâ=ânegative control, unexposed HDF. Error bars represent standard error (nâ=â4).
Figure 3. Effect of the sunscreens on the development of embryos of P. lividus. (A) Percentages of P. lividus anomalous embryos after exposure to Sunscreens A, B and C at different concentration (10, 20 and 50âµLâLâ1) over time. Error bars represent standard deviation (nâ=â3). (B) Unexposed embryos at the start of the experiment where the elevated fertilization layer is visible (a); first divisions into blastomeres observed after 70âmin (bâd), blastula stage observed after 6âh (e) and gastrula stage observed after 24âh from the beginning of the experiment (f). Abnormal embryos characterized by asymmetrical division into blastomeres and superficial blebs (gâi), signs of cell necrosis (l and n) and esogastrula (m) found in early developmental stages after exposure to sunscreens at the different concentrations. Scale bar: 80âμm.
Figure 4. Effect of the sunscreens on the development of larvae of P. lividus. (A) Percentages of P. lividus anomalous larvae after exposure to Sunscreens (A,B and C), at different concentration (10, 20 and 50âµLâLâ1) over time. Error bars represent standard deviation (nâ=â3). (B) Unexposed larva, control (a). Main anomalies found in P. lividus larvae after different exposure times: joined anterior arms (b), crossed skeletal tips at the hood apex (c), incomplete skeletal roots (d). Scale bar: 100âμm.
Figure 5. Effects of Sunscreens (A,B and C), at the concentration of 50âµLâLâ1, on AChE activity of larvae of P. lividus compared to the control (square symbols). Error bars represent standard deviation (nâ=â3).
Aluigi,
Dose-dependent effects of chlorpyriphos, an organophosphate pesticide, on metamorphosis of the sea urchin, Paracentrotus lividus.
2010, Pubmed,
Echinobase
Aluigi,
Dose-dependent effects of chlorpyriphos, an organophosphate pesticide, on metamorphosis of the sea urchin, Paracentrotus lividus.
2010,
Pubmed
,
Echinobase
Amemiya,
Complete regulation of development throughout metamorphosis of sea urchin embryos devoid of macromeres.
1996,
Pubmed
,
Echinobase
Brugè,
Reference gene validation for qPCR on normoxia- and hypoxia-cultured human dermal fibroblasts exposed to UVA: is β-actin a reliable normalizer for photoaging studies?
2011,
Pubmed
Brugè,
A comparative study on the possible cytotoxic effects of different nanostructured lipid carrier (NLC) compositions in human dermal fibroblasts.
2015,
Pubmed
Brugè,
Prevention of UVA-induced oxidative damage in human dermal fibroblasts by new UV filters, assessed using a novel in vitro experimental system.
2014,
Pubmed
Buechner,
Changes of MMP-1 and collagen type Ialpha1 by UVA, UVB and IRA are differentially regulated by Trx-1.
2008,
Pubmed
Burnett,
Current sunscreen controversies: a critical review.
2011,
Pubmed
Calafat,
Concentrations of the sunscreen agent benzophenone-3 in residents of the United States: National Health and Nutrition Examination Survey 2003--2004.
2008,
Pubmed
Carballeira,
Identification of specific malformations of sea urchin larvae for toxicity assessment: application to marine pisciculture effluents.
2012,
Pubmed
,
Echinobase
Carballeira,
Implementation of a minimal set of biological tests to assess the ecotoxic effects of effluents from land-based marine fish farms.
2012,
Pubmed
,
Echinobase
Castellano,
Shedding light on ovothiol biosynthesis in marine metazoans.
2016,
Pubmed
,
Echinobase
Danovaro,
Sunscreens cause coral bleaching by promoting viral infections.
2008,
Pubmed
Danovaro,
Sunscreen products increase virus production through prophage induction in marine bacterioplankton.
2003,
Pubmed
Diffey,
Sunscreens and melanoma: the future looks bright.
2005,
Pubmed
Dondi,
Interactions between different solar UVB/UVA filters contained in commercial suncreams and consequent loss of UV protection.
2006,
Pubmed
Doney,
Climate change impacts on marine ecosystems.
2012,
Pubmed
Downs,
Toxicopathological Effects of the Sunscreen UV Filter, Oxybenzone (Benzophenone-3), on Coral Planulae and Cultured Primary Cells and Its Environmental Contamination in Hawaii and the U.S. Virgin Islands.
2016,
Pubmed
Drews,
Cholinesterase in embryonic development.
1975,
Pubmed
,
Echinobase
ELLMAN,
A new and rapid colorimetric determination of acetylcholinesterase activity.
1961,
Pubmed
Falugi,
Sea urchin development: an alternative model for mechanistic understanding of neurodevelopment and neurotoxicity.
2008,
Pubmed
,
Echinobase
Fent,
A tentative environmental risk assessment of the UV-filters 3-(4-methylbenzylidene-camphor), 2-ethyl-hexyl-4-trimethoxycinnamate, benzophenone-3, benzophenone-4 and 3-benzylidene camphor.
2010,
Pubmed
Gambardella,
Developmental abnormalities and changes in cholinesterase activity in sea urchin embryos and larvae from sperm exposed to engineered nanoparticles.
2013,
Pubmed
,
Echinobase
Gambardella,
Multidisciplinary screening of toxicity induced by silica nanoparticles during sea urchin development.
2015,
Pubmed
,
Echinobase
Gaw,
Sources, impacts and trends of pharmaceuticals in the marine and coastal environment.
2014,
Pubmed
Gonzalez,
Photostability of commercial sunscreens upon sun exposure and irradiation by ultraviolet lamps.
2007,
Pubmed
Guillou,
Comparison of embryonic development and metal contamination in several populations of the sea urchin Sphaerechinus granularis (Lamarck) exposed to anthropogenic pollution.
2000,
Pubmed
,
Echinobase
Halpern,
A global map of human impact on marine ecosystems.
2008,
Pubmed
Kim,
Occurrences, toxicities, and ecological risks of benzophenone-3, a common component of organic sunscreen products: a mini-review.
2014,
Pubmed
Krause,
Sunscreens: are they beneficial for health? An overview of endocrine disrupting properties of UV-filters.
2012,
Pubmed
Kunz,
Multiple hormonal activities of UV filters and comparison of in vivo and in vitro estrogenic activity of ethyl-4-aminobenzoate in fish.
2006,
Pubmed
Langford,
Inputs of chemicals from recreational activities into the Norwegian coastal zone.
2008,
Pubmed
Maipas,
Sun lotion chemicals as endocrine disruptors.
2015,
Pubmed
Manzo,
Embryotoxicity and spermiotoxicity of nanosized ZnO for Mediterranean sea urchin Paracentrotus lividus.
2013,
Pubmed
,
Echinobase
Mesarič,
Sperm exposure to carbon-based nanomaterials causes abnormalities in early development of purple sea urchin (Paracentrotus lividus).
2015,
Pubmed
,
Echinobase
Minetto,
Ecotoxicity of engineered TiO2 nanoparticles to saltwater organisms: an overview.
2014,
Pubmed
Narayanan,
Ultraviolet radiation and skin cancer.
2010,
Pubmed
Osterwalder,
Global state of sunscreens.
2014,
Pubmed
Paredes,
Ecotoxicological evaluation of four UV filters using marine organisms from different trophic levels Isochrysis galbana, Mytilus galloprovincialis, Paracentrotus lividus, and Siriella armata.
2014,
Pubmed
,
Echinobase
Pesando,
Biological targets of neurotoxic pesticides analysed by alteration of developmental events in the Mediterranean sea urchin, Paracentrotus lividus.
2003,
Pubmed
,
Echinobase
Peterson,
Primary mesenchyme cell patterning during the early stages following ingression.
2003,
Pubmed
,
Echinobase
Prichard,
Effects of pharmaceuticals and personal care products on marine organisms: from single-species studies to an ecosystem-based approach.
2016,
Pubmed
Ruocco,
New insights into negative effects of lithium on sea urchin Paracentrotus lividus embryos.
2016,
Pubmed
,
Echinobase
Sánchez-Quiles,
Sunscreens as a source of hydrogen peroxide production in coastal waters.
2014,
Pubmed
Sánchez-Quiles,
Are sunscreens a new environmental risk associated with coastal tourism?
2015,
Pubmed
Schlumpf,
Endocrine activity and developmental toxicity of cosmetic UV filters--an update.
2004,
Pubmed
Serra-Roig,
Occurrence, fate and risk assessment of personal care products in river-groundwater interface.
2016,
Pubmed
Tovar-Sánchez,
Sunscreen products as emerging pollutants to coastal waters.
2013,
Pubmed
Venditti,
In vitro photostability and photoprotection studies of a novel 'multi-active' UV-absorber.
2008,
Pubmed
Wondrak,
Endogenous UVA-photosensitizers: mediators of skin photodamage and novel targets for skin photoprotection.
2006,
Pubmed