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1 he most (86.4% of all visits associated with sunscreen).
2 s soy isoflavones, and even moisturizers and sunscreen.
3 ildren, especially the use of broad-spectrum sunscreen.
4 inoids, which have significant toxicity, and sunscreen.
5 protected by either a physical barrier or a sunscreen.
6 inoids, which have significant toxicity, and sunscreen.
7 ion against cumulative erythema than the UVB sunscreen.
8 , which developed in 1 participant with each sunscreen.
9 likely to be biosynthetic precursors of the sunscreen.
10 t individuals should refrain from the use of sunscreen.
11 t individuals should refrain from the use of sunscreen.
12 ation and using photoprotective clothing and sunscreens.
13 sed by younger children are moisturizers and sunscreens.
14 such as sediment pore water, wastewater, and sunscreens.
15 rds for broad-spectrum coverage to be met by sunscreens.
16 ng some of the additional safety studies for sunscreens.
17 (UV) radiation, including the proper use of sunscreens.
18 ly lower than that achieved by using topical sunscreens.
19 me, air fresheners, and dryer sheets) and in sunscreens.
20 posure is the biosynthesis of small-molecule sunscreens.
21 elanoma and use of the newer formulations of sunscreens.
22 ting step in the synthesis of sinapate ester sunscreens.
23 otective clothing and eyeware in addition to sunscreens.
24 cation of an immune protection factor to all sunscreens.
25 cern for current cinnamate ester-based human sunscreens.
26 ving some nonclinical toxicology studies for sunscreens.
27 found in nature and those used in commercial sunscreens.
28 pectrum, SPF >/=30, and water resistant) for sunscreens.
29 ) is one of the UV filters commonly found in sunscreens.
32 n and older individuals reported less use of sunscreen (32.7% vs 35.5%; F = 5.36; P = .02) and hats (
33 thema dose, on gluteal skin, with or without sunscreen, 48 h prior to sensitization with dinitrochlor
34 otection practices, including regular use of sunscreen (53.3%, 45.1%, and 38.1%, respectively) and we
35 fish may produce and use this molecule as a sunscreen.(6) We generated a gadusol-deficient mutant ze
36 y assist in explaining discrepancies between sunscreens' abilities to protect against erythema and ph
38 as the potential to be a coral reef-friendly sunscreen active ingredient that can provide broad-spect
39 inistration (FDA) has provided guidance that sunscreen active ingredients with systemic absorption gr
40 dy demonstrated the systemic absorption of 4 sunscreen active ingredients; additional studies are nee
41 study reveals why human NAT1 acetylates the sunscreen additive p-aminobenzoic acid and tobacco smoke
42 ss likely than Chinese participants to apply sunscreen (adjusted odds ratio [aOR], 0.55; 95% CI, 0.41
44 e properties of T-Lite SF, a TiO2-NC used as sunscreen, after weathering in water and under light.
47 hese compounds, which are used in commercial sunscreen agents due to a high absorption in the ultravi
48 e first study to investigate the presence of sunscreen agents in tissue liver of Franciscana dolphin
49 Modulators of the UV-tanning pathway include sunscreen agents, melanocortin 1 receptor activators, ad
53 sunscreen and placebo, discretionary use of sunscreen and 30 mg of beta-carotene, and discretionary
54 t into 4 groups: daily use of broad-spectrum sunscreen and 30 mg of beta-carotene, daily use of sunsc
55 ering yeast to efficiently produce a natural sunscreen and antioxidant presents an avenue for its lar
56 microtopography between 1992 and 1996 in the sunscreen and beta-carotene groups compared with control
57 rts aimed at UV protection, including use of sunscreen and clothing, annual cases of skin cancer cont
58 of sunburn) and alerts (to apply or reapply sunscreen and get out of the sun), hourly UV Index, and
60 lfonic acid, indicating organic compounds in sunscreen and other personal care products as sources of
61 t (UV) radiation filters, given their use in sunscreen and personal-care products and their reported
62 een and 30 mg of beta-carotene, daily use of sunscreen and placebo, discretionary use of sunscreen an
64 nin is a brown-black biological pigment with sunscreen and radical scavenging functions important to
65 ol-containing emollient or patch, as well as sunscreen and skin-care products for prevention of skin
66 er butyl methoxydibenzoylmethane, the SPF 15 sunscreen and the UVA filter together, and the lotion ve
68 , the UVA filter, and the combination SPF 15 sunscreen and UVA filter, resulting in increasing degree
69 g paid to prevention through the use of both sunscreens and after sun treatments, many of which conta
72 a new proposed rule in 2019 (84.FR.6204) for sunscreens and identified the need for additional safety
75 t users of seawater swimming pools may apply sunscreens and other personal-care products containing o
76 Organic ultraviolet (UV) filters are used in sunscreens and other personal-care products to protect a
77 tion of ultraviolet-induced p53 mutations by sunscreens and protection against skin cancer using an e
79 e review the interplay between UV radiation, sunscreens and the skin, highlighting current controvers
80 lf century, initially as a putative "natural sunscreen" and later as a mediator of photoimmunosuppres
81 automotive lubricants, clothing, deodorants, sunscreens, and cosmetics and can potentially accumulate
82 n consumer products, for example, cosmetics, sunscreens, and electrical devices, has increased tremen
83 ated pigmentary disorders, the proper use of sunscreens, and the treatment of depigmented lesions.
85 n a clinical pharmacology unit and examining sunscreen application among healthy participants, all 6
88 indoors were more likely to rarely/never use sunscreen (aPR, 1.34; 95% CI, 1.11-1.62), protective clo
91 against immunosuppression may be improved if sunscreens are formulated to offer equivalent protection
93 r is ultraviolet radiation from the sun, but sunscreens are often used in a suboptimal manner, compro
95 her genistein nor n-acetyl cysteine acted as sunscreens as they had no effect on ultraviolet-induced
96 UV filter, which is used in the majority of sunscreens as well as other personal care products (PCP)
100 the rate at which physicians are mentioning sunscreen at patient visits is quite low, even for patie
102 ad teachers allow time for students to apply sunscreen at school, and 11.8% of high schools (95% CI,
104 PF is much more reliable with broad-spectrum sunscreens because SPF with primarily UVB sunscreens is
105 sked parents to ensure that students applied sunscreen before school (16.4%; 95% CI, 12.9%-20.6%).
107 vestigated the genetic basis for mycosporine sunscreen biosynthesis by the cyanobacterium Nostoc punc
108 with self-reported use of liquid soap (TCS), sunscreen (BP-3), lotion (BP-3 and parabens), and cosmet
111 ble fraction) with general use of SPF >/= 15 sunscreens by women age 40 to 75 years was 18% (95% CI,
112 a novel method to establish the efficacy of sunscreens, by measuring ultraviolet-A-induced free-radi
114 nal care products (PCPs) such as lotions and sunscreens can serve as precursors to form additional HB
115 rall "safe sun strategy" in which the use of sunscreens certainly must be accompanied by other protec
119 rsonal care products, toothpastes and select sunscreens contained 1% to >10% titanium by weight.
120 Pretreatment with a photostable UVA/UVB sunscreen containing an antioxidant combination signific
121 filter had no protective effect, whereas, a sunscreen containing both ultraviolet A and ultraviolet
122 skin of our transgenic mice that included: a sunscreen containing octyl methoxycinnamate and benzophe
123 with human activities and use of lotions and sunscreens, containing organic UV-filters, in addition t
125 l, while applying both NPs and NP-formulated sunscreens could significantly reduce DNA damage, result
128 e light-induced ROS, suggesting that UVA/UVB sunscreens do not protect the skin from visible light-in
129 lth policy makers facing decisions regarding sunscreen education campaigns and sets the stage for fut
131 ential risks; however, optimizing the use of sunscreens, especially among children and adolescents, r
134 These complex natural products may act as sunscreens for the producing organism, thus offering pro
137 for optimal protection against skin damage, sunscreen formulations should filter all UV wavelengths,
138 tive ingredients administered in 4 different sunscreen formulations were systemically absorbed and ha
145 ly sunscreen group than in the discretionary sunscreen group (relative odds, 0.76 [95% CI, 0.59 to 0.
147 e end of the trial was 24% less in the daily sunscreen group than in the discretionary sunscreen grou
150 reas the low ultraviolet A protection factor sunscreen had an immune protection factor of 15, which w
151 hat the high ultraviolet A protection factor sunscreen had an immune protection factor of 50, more th
153 lar compound called gadusol, whose role as a sunscreen has yet to be tested despite its discovery ove
156 assembly of scytonemin (1), a cyanobacterial sunscreen, have identified beta-ketoacid 2 as an importa
158 PO(4)(3-), and N-NO(3)(-)) from a commercial sunscreen in seawater, and the role of UV radiation in t
159 th body exposure or the number of days using sunscreen in the second and third years of follow-up.
160 ar water.(3) While melanin is the only known sunscreen in vertebrates, it often emerges late in embry
161 sponse were generated either with or without sunscreen in vivo and protection factors were derived fo
164 e high- with low-sun protection factor (SPF) sunscreens in relation to sunbathing habits in a large c
166 titanium dioxide nanoparticles stemming from sunscreens in the suspended matter of the lake using ele
167 protection efficacy conferred by commercial sunscreens, in terms of induction of DNA lesions and cel
172 ing prospect that nature's selection of UV-B sunscreen is based in part on the inherent quantum mecha
173 um sunscreens because SPF with primarily UVB sunscreens is dependent on time of day and latitude.
177 protection from cumulative sunburn with two sunscreens labeled SPF 6, but with different UVR-absorbi
178 ch was attributed to a high concentration of sunscreen lotions in a small recirculated water volume.
179 ng/g) were found in skin lotions (including sunscreen lotions), followed by makeup products (284; 22
180 ere applied to the detection of TiO(2) NP in sunscreen lotions, rainwaters, and swimming pool waters.
183 ng of the photophysics and photochemistry of sunscreen molecules selected by nature could aid the des
185 alyses, however, are not able to distinguish sunscreen nanoparticles from natural Ti-bearing nanopart
190 lso known as BP-3 or oxybenzone) is added to sunscreens, plastics, and some coatings to filter UV rad
191 development in all the mice treated with the sunscreens plus 1000 kJ ultraviolet B per m2 was 2% and
192 violet B per m2 was 2% and mice treated with sunscreens plus 1500 kJ ultraviolet B per m2 was 15%.
194 ively, but less than 5% of mice treated with sunscreens plus ultraviolet showed evidence of p53 mutat
196 ed immunoprotection afforded by a commercial sunscreen preparation (labeled sun protection factor 15)
198 de nanoparticle content in 1 g of commercial sunscreen produces rates of H2O2 in seawater of up to 46
200 AVB), a simple boron complex of a commercial sunscreen product, exhibits morphology-dependent emissio
204 itro methodologies used for the selection of sunscreen products for an FDA-sponsored proof-of-concept
205 titanium dioxide nanomaterials released from sunscreen products into the Old Danube Lake (Vienna, Aus
207 tudies detailing the environmental impact of sunscreen products on coastal ecosystems are considered
211 ic contact reactions to UV filters, personal sunscreen products, and nonsteroidal anti-inflammatory d
215 consistently demonstrated that all the test sunscreens protected beyond their designated sun protect
217 lidates public health campaigns that promote sunscreen protection for individuals at risk of melanoma
218 ry methods for investigating the efficacy of sunscreen protection of epidermal immune function use th
221 ain Outcomes and Measures: Rare/never use of sunscreen, protective clothing, shade; multiple sunburns
224 times the minimal erythema dose, with either sunscreen, resulted in comparable levels of thymine dime
225 ies of a secondary metabolite, the microbial sunscreen scytonemin, produced by a group of late-succes
227 ; sun-protective behaviors included applying sunscreen, staying under shade, wearing long-sleeved shi
228 have suggested a lack of correlation between sunscreen sun protection factor and protection of the sk
229 the protection afforded by three high factor sunscreens (sun protection factor 20+) that claim ultrav
230 onmentally relevant light source, we applied sunscreens (sun protection factors 15-22) on to the shav
231 ved shirts but less likely to sunburn, apply sunscreen, tan indoors, and receive TBSE than Non-Hispan
233 pression was the observation that applying a sunscreen that contained an ultraviolet B only filter ha
235 ow that the metabolites serve as Lysobacter "sunscreens" that are important for the survival of these
237 Scytonemin is a heterocyclic indole-alkaloid sunscreen, the synthesis of which is induced upon exposu
238 acetyl transferase activity with the SPF 15 sunscreen, the UVA filter, and the combination SPF 15 su
240 s and that applying sun protection factor 15 sunscreens to mouse skin before each Kodacel-filtered FS
243 ectrum can be used to predict the ability of sunscreens to protect against UVR-induced cis-UCA format
244 t both end-points, which supports the use of sunscreens to reduce immunosuppression but protection ag
245 as a means of covalently binding UVA and UVB sunscreens to the outer layer of skin to provide long-la
250 ers, application of 4 commercially available sunscreens under maximal use conditions resulted in plas
251 the shade, 41.0% vs 33.7%; P = .03) but less sunscreen use (mean days, 28.6% vs 34.5%; P = .048) than
252 was used to estimate the association between sunscreen use (never, SPF < 15, SPF >/= 15) and melanoma
254 ence does not support an association between sunscreen use and melanoma, systemic toxicity or vitamin
256 ement to provide patient education regarding sunscreen use and sun-protective behaviors, the rate at
257 rpose To assess melanoma risk in relation to sunscreen use and to compare high- with low-sun protecti
258 n the basis of 1 fair-quality trial, regular sunscreen use can prevent squamous cell carcinoma, but i
260 sun sensitivity and childhood exposures, and sunscreen use has been promoted for prevention of skin c
262 tors/angiotensin receptor blockers, and more sunscreen use in the week, but not the 6 months, before
265 aluating the cost-effectiveness of promoting sunscreen use to prevent actinic keratoses and nonmelano
268 tude, time of day, skin pigmentation, aging, sunscreen use, and glass all influence the cutaneous pro
270 lexity of measuring ultraviolet exposure and sunscreen use, and inadequate adjustment for important c
271 sun exposure and were more likely to report sunscreen use, suggesting specific sun exposure profiles
281 hade and wearing sun-protective clothing and sunscreen) using a 5-point Likert scale, duration of out
282 e (39 [17.0%]), educational aid (20 [8.7%]), sunscreen/UV recommendation (19 [8.3%]), calculator (12
285 by eye and objectively, and the SPF of each sunscreen was modeled with changes in solar UVR with tim
286 were determined in vitro and showed that the sunscreen was primarily an ultraviolet B absorber, with
289 let radiation wavelengths transmitted by the sunscreen were determined in vitro and showed that the s
291 each umbrella compared with that provided by sunscreen with a high sun protection factor under actual
295 immune suppression and that a broad-spectrum sunscreen with high ultraviolet A filtering capacity res
299 entrations for three individuals having used sunscreen within 5 days prior to sample collection.
300 then increased ultraviolet A filtration by a sunscreen would better protect the immune system during