Relatively little is known about the exposure of nail
technicians
to semivolatile organic compounds (SVOCs) in nail salons. We collected
preshift and postshift urine samples and silicone wrist bands (SWBs)
worn on lapels and wrists from 10 female nail technicians in the Boston
area in 2016–17. We analyzed samples for phthalates, phthalate
alternatives, and organophosphate esters (OPEs) or their metabolites.
Postshift urine concentrations were generally higher than preshift
concentrations for SVOC metabolites; the greatest change was for a
metabolite of the phthalate alternative di(2-ethylhexyl) terephthalate
(DEHTP): mono(2-ethyl-5-carboxypentyl) terephthalate (MECPTP) more
than tripled from 11.7 to 36.6 μg/g creatinine. DEHTP biomarkers
were higher in our study participants’ postshift urine compared
to 2015–2016 National Health and Nutrition Examination Survey
females. Urinary MECPTP and another DEHTP metabolite were moderately
correlated (r = 0.37–0.60) with DEHTP on the
SWBs, suggesting occupation as a source of exposure. Our results suggest
that nail technicians are occupationally exposed to certain phthalates,
phthalate alternatives, and OPEs, with metabolites of DEHTP showing
the largest increase across a work day. The detection of several of
these SVOCs on SWBs suggests that they can be used as a tool for examining
potential occupational exposures to SVOCs among nail salon workers.
In
the 2000s, nail polish manufacturers started promoting “3-Free”
products, phasing out three widely publicized toxic chemicals: toluene,
formaldehyde, and dibutyl phthalate (DnBP). However, DnBP was
sometimes replaced by another endocrine-disrupting plasticizer,
triphenyl phosphate (TPHP). Many new “n-Free”
labels have since appeared, without any standardization on which n chemicals are excluded. This study aimed to compare measured
plasticizer content against nail polish labels. First, we summarized
definitions of labels. Then, we measured 12 phthalate and 10 organophosphate
plasticizers in 40 nail polishes from 12 brands selected for popularity
and label variety. We found labels ranging from 3- to 13-Free; 10-Free
was the most inconsistently defined (six definitions). Our samples
contained TPHP and bis(2-ethylhexyl) phthalate (DEHP) at up to 7940
and 331 μg/g, respectively. The 5- to 13-Free samples had lower
TPHP levels than unlabeled or 3-Free samples (median <0.002 vs
3730 μg/g, p < 0.001). The samples that
did not contain TPHP had higher DEHP levels (median 68.5 vs 1.51 μg/g, p < 0.05). We measured plasticizers above 100 μg/g
in five brands that did not disclose them and in two that excluded
them in labels. This study highlights inconsistencies in nail polish
labels and identifies TPHP and DEHP as ingredient substitutes for
DnBP.
With mounting e-waste, more workers, their family members, and communities could experience unhealthful exposures to metals and other chemicals. We identified research needs to further assess exposures, health, and improve controls. The long-term solution is manufacturing of electronics without harmful substances and easy-to-disassemble components.
Many metals found in electronic scrap are known to cause serious health effects, including but not limited to cancer and respiratory, neurologic, renal, and reproductive damage. The National Institute for Occupational Safety and Health, Centers for Disease Control and Prevention performed three health hazard evaluations at electronic scrap recycling facilities in the U.S. to characterize employee exposure to metals and recommend control strategies to reduce these exposures. We performed air, surface, and biological monitoring for metals. We found one overexposure to lead and two overexposures to cadmium. We found metals on non-production surfaces, and the skin and clothing of workers before they left work in all of the facilities. We also found some elevated blood lead levels (above 10 micrograms per deciliter), however no employees at any facility had detectable mercury in their urine or exceeded 34% of the OELs for blood or urine cadmium. This article focuses on sampling results for lead, cadmium, mercury, and indium. We provided recommendations for improving local exhaust ventilation, reducing the recirculation of potentially contaminated air, using respirators until exposures are controlled, and reducing the migration of contaminants from production to non-production areas. We also recommended ways for employees to prevent taking home metal dust by using work uniforms laundered on-site, storing personal and work items in separate lockers, and using washing facilities equipped with lead-removing cleaning products.
Perchloroethylene (PERC) is the most common solvent used for dry cleaning in the United States. PERC is a reproductive toxicant, neurotoxicant, potential human carcinogen, and a persistent environmental pollutant. The Environmental Protection Agency is evaluating PERC under the Frank R. Lautenberg Chemical Safety for the 21st Century Act, which amended the Toxic Substances Control Act (amended TSCA), and has mandated that PERC dry cleaning machines be removed from residential buildings. Some local and state programs are also requiring or facilitating transitions to alternative cleaning technologies. However, the potential for these alternatives to harm human health and the environment is not well-understood. This review describes the issues surrounding the use of PERC and alternative solvents for dry cleaning while highlighting the lessons learned from a local government program that transitioned PERC dry cleaners to the safest current alternative: professional wet cleaning. Implications for future public health research and policy are discussed: (1) we must move away from PERC, (2) any transition must account for the economic instability and cultural aspects of the people who work in the industry, (3) legacy contamination must be addressed even after safer alternatives are adopted, and (4) evaluations of PERC alternatives are needed to determine their implications for the long-term health and sustainability of the people who work in the industry.
The National Institute for Occupational Safety and Health (NIOSH) surveyed a randomly selected sample of electronic scrap (e-scrap) recycling facilities nationwide to characterize work processes, exposures, and controls. Despite multiple attempts to contact 278 facilities, only 47 responded (17% response rate). Surveyed facilities reported recycling a wide variety of electronics. The most common recycling processes were manual dismantling and sorting. Other processes included shredding, crushing, and automated separation. Many facilities reported that they had health and safety programs in place. However, some facilities reported the use of compressed air for cleaning, a practice that can lead to increased employee dust exposures, and some facilities allowed food and drinks in the production areas, a practice that can lead to ingestion of contaminants. Although our results may not be generalizable to all US e-scrap recycling facilities, they are informative regarding health and safety programs in the industry. We concluded that e-scrap recycling has the potential for a wide variety of occupational exposures particularly because of the frequent use of manual processes. On-site evaluations of e-scrap recyclers are needed to determine if reported work processes, practices, and controls are effective and meet current standards and guidelines. Educating the e-scrap recycling industry about health and safety best practices, specifically related to safe handling of metal dust, would help protect employees.
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