Arsenic is a ubiquitous, naturally occurring metalloid that may be a significant risk factor for cancer after exposure to contaminated drinking water, cigarettes, foods, industry, occupational environment, and air. Among the various routes of arsenic exposure, drinking water is the largest source of arsenic poisoning worldwide. Arsenic exposure from ingested foods usually comes from food crops grown in arsenic-contaminated soil and/or irrigated with arsenic-contaminated water. According to a recent World Health Organization report, arsenic from contaminated water can be quickly and easily absorbed and depending on its metabolic form, may adversely affect human health. Recently, the US Food and Drug Administration regulations for metals found in cosmetics to protect consumers against contaminations deemed deleterious to health; some cosmetics were found to contain a variety of chemicals including heavy metals, which are sometimes used as preservatives. Moreover, developing countries tend to have a growing number of industrial factories that unfortunately, harm the environment, especially in cities where industrial and vehicle emissions, as well as household activities, cause serious air pollution. Air is also an important source of arsenic exposure in areas with industrial activity. The presence of arsenic in airborne particulate matter is considered a risk for certain diseases. Taken together, various potential pathways of arsenic exposure seem to affect humans adversely, and future efforts to reduce arsenic exposure caused by environmental factors should be made.
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Evaluation of in utero exposure to arsenic in South Africa Halina B. Röllin, Kalavati Channa, Bukola G. Olutola, Jon Ø. Odland Science of The Total Environment.2017; 575: 338. CrossRef
Arsenic removal by electrocoagulation process: Recent trends and removal mechanism P.V. Nidheesh, T.S. Anantha Singh Chemosphere.2017; 181: 418. CrossRef
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Hepatoprotective Role of Hydrangea macrophylla against Sodium Arsenite-Induced Mitochondrial-Dependent Oxidative Stress via the Inhibition of MAPK/Caspase-3 Pathways Md Akanda, Hyun-Jin Tae, In-Shik Kim, Dongchoon Ahn, Weishun Tian, Anowarul Islam, Hyeon-Hwa Nam, Byung-Kil Choo, Byung-Yong Park International Journal of Molecular Sciences.2017; 18(7): 1482. CrossRef
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Evaluation of epigenetic alterations (mir-126 and mir-155 expression levels) in Mexican children exposed to inorganic arsenic via drinking water Mónica S. Pérez-Vázquez, Ángeles C. Ochoa-Martínez, Tania RuÍz-Vera, Yesenia Araiza-Gamboa, Iván N. Pérez-Maldonado Environmental Science and Pollution Research.2017; 24(36): 28036. CrossRef
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Estimation of Inorganic Arsenic Exposure in Populations With Frequent Seafood Intake: Evidence From MESA and NHANES Miranda R. Jones, Maria Tellez-Plaza, Dhananjay Vaidya, Maria Grau, Kevin A. Francesconi, Walter Goessler, Eliseo Guallar, Wendy S. Post, Joel D. Kaufman, Ana Navas-Acien American Journal of Epidemiology.2016; 184(8): 590. CrossRef
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Assessment of Arsenic Levels in Body Samples and Chronic Exposure in People Using Water with a High Concentration of Arsenic: a Field Study in Kutahya Inci Arikan, Nazli Dizen Namdar, Cuneyt Kahraman, Merve Dagci, Ezgi Ece Asian Pacific Journal of Cancer Prevention.2015; 16(8): 3183. CrossRef
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OBJECTIVES This study was carried out to investigate the prevalence and symptoms related to hair dyeing among university freshmen. METHODS: The authors conducted a questionnaire survey among 1, 499 university freshmen from Mar 11 to 15, 2002. RESULTS: The study group contained 710 females and 789 males. Up until 2002, 62.7% of the subjects had experienced hair dyeing, and this was significantly higher in females (66.2%, p< 0.05). The period of first experience of hair dyeing was in high school for 361 cases (38.4%), after high school for 345 cases (36.7%) and before high school for 234 cases (24.9%). The major reasons of hair dyeing were 'to improve their appearance' in 466 cases (49.6%), and 'to follow the hair dyeing fashion' in 169 cases (18.0%). The prevalence of hair dyeing in 2002 was 47.8%, and again was significantly higher in females (53.7%, p< 0.05). The major symptoms related to hair dyeing were 'cleaved and nonelastic hair' in 498 cases (69.6%), and 'thin and easily breakable hair' in 353 cases (49.3%). Of those, 361 cases (50.4%) appealed to three or more symptoms related to hair dyeing. Through multiple logistic regression, factors significantly associated with symptoms related to hair dyeing were found to be female (OR=2.14, 95% CI; 1.61-2.83), use of hair dryer (OR=1.36, 95% CI; 1.004-1.854), a frequency of hair dyeing of three or more (OR=1.48, 95% CI; 1.04-2.09), and a duration of processing hair dyeing of over 60 minutes (OR=2.18, 95% CI; 1.50-3.18). CONCLUSIONS: The prevalence and experience of hair dyeing were generally high among university freshmen. Therefore, more extensive epidemiological studies on the symptoms related to hair dyeing should be conducted.
This study aims at providing the fundamental data on the field of cosmetics by comparing heavy metal concentration in terms of domestic / foreign products, items, companies and colors. This study has determined the concentration of chromium, lead, mangagnese, nickel, copper and vanadium in cosmetics such as moisturizer, concealer, foundation (Ivory-yellow), compact powder (Ivory-yellow), lip color (Red, brown), eye shadow (Red, brwon and dark green) and eye liner (Black) manufactured by five domestic cosmetic companies and five foreign cosmetic companies on the market. The samples have been collected in cosmetic stores in Pusan from Dec. lst 1996 to Jan. 3lst 1997. The results are as follows : 1. The heavy metal concentration in cosmetics was 2.42ng/g for chromium, 0.82ng/g for lead, 4.49ng/g for manganese, 1.69ng/g for nickel, 0.53ng/g for copper, and 0.51ng/g for vanadium, respectively. 2. Lead and vanadium concentration were significantly higher in domestic cosmetics than foreign cosmetics(p<0.05). 3. The mean(GM) concentrations of heavy metal were different significantly (p<0.01) when classified with cosmetic items. The highest means shown at eye shadow in Cr (14.96ng/g), Cu (1.32ng/g), V (1.28ng/g), and Ni (8.30ng/g), compact powder in Pb(2.50ng/g), eye liner in Mn(90.62ng/g). 4. The mean(GM) concentrations of heavy metal were different significantly (p<0.01) among colored cosmetics. The highest mean concentration of Cr, Ni, Cu and V were dark green- colored cosmetics, that of Mn was black-colored cosmetics, and that of Pb was ivory yellow-colored cosmetics.