Human systemic exposure to [¹4C]-paraphenylenediamine-containing oxidative hair dyes: Absorption, kinetics, metabolism, excretion and safety assessment.

Systemic exposure was measured in humans after hair dyeing with oxidative hair dyes containing 2.0% (A) or 1.0% (B) [(14)C]-p-phenylenediamine (PPD). Hair was dyed, rinsed, dried, clipped and shaved; blood and urine samples were collected for 48 hours after application. [(14)C] was measured in all materials, rinsing water, hair, plasma, urine and skin strips. Plasma and urine were also analysed by HLPC/MS/MS for PPD and its metabolites (B). Total mean recovery of radioactivity was 94.30% (A) or 96.21% (B). Mean plasma Cmax values were 132.6 or 97.4 ng [(14)C]-PPDeq/mL, mean AUC(0-∞) values 1415 or 966 ng [(14)C]-PPDeq/mL*hr in studies A or B, respectively. Urinary excretion of [(14)C] mainly occurred within 24 hrs after hair colouring with a total excretion of 0.72 or 0.88% of applied radioactivity in studies A or B, respectively. Only N,N'-diacetylated-PPD was detected in plasma and the urine. A TK-based human safety assessment estimated margins of safety of 23.3- or 65-fold relative to respective plasma AUC or Cmax values in rats at the NOAEL of a toxicity study. Overall, hair dyes containing PPD are unlikely to pose a health risk since they are used intermittently and systemic exposure is limited to the detoxified metabolite N,N'-diacetyl-PPD.

Occupational exposure of hairdressers to [14C]-para-phenylenediamine-containing oxidative hair dyes: a mass balance study.

We monitored the exposure of hairdressers to oxidative hair dyes for 6 working days under controlled conditions. Eighteen professional hairdressers (3/day) coloured hairdresser's training heads bearing natural human hair (hair length: approximately 30 cm) for 6 h/working day with a dark-shade oxidative hair dye containing 2% [14C]-para-phenylenediamine (PPD). Three separate phases of hair dyeing were monitored: (A) dye preparation/hair dyeing, (B) rinsing/shampooing/conditioning and (C) cutting/drying/styling. Ambient air and personal monitoring samples (vapours and particles), nasal and hand rinses were collected during all study phases. Urine (pre-exposure, quantitative samples for the 0-12, 12-24, 24-48 h periods after start of exposure) and blood samples (blank, 4, 8 or 24 h) were collected from all exposed subjects. Radioactivity was determined in all biological samples and study materials, tools and washing liquids, and a [14C]-mass balance was performed daily. No adverse events were noted during the study. Waste, equipment, gloves and coveralls contained 0.41+/-0.16%, dye mixing bowls 2.88+/-0.54%, hair wash 45.47+/-2.95%, hair+scalp 53.46+/-4.06% of the applied radioactivity, respectively. Plasma levels were below the limit of quantification (10 ng PPDeq/mL). Total urinary 0-48 h excretion of [14C] levels ranged from a total of <2-18 microg PPDeq and was similar in subjects exposed during the different phases of hair dyeing. Minimal air levels at or slightly above the limit of quantification were found in a few personal air monitoring samples during the phases of hair dyeing and hair cutting, but not during the rinsing phase. Air area monitoring samples or nasal rinses contained no measurable radioactivity. Hand residues ranged from 0.006 to 0.15 microg PPDeq/cm2, and were found predominantly after the cutting/drying phase. The mean mass balance of [14C] across the six study days was 102.50+/-2.20%. Overall, the mean, total systemic exposure of hairdressers to oxidative hair dyes during a working day including 6 hair dyeing processes was estimated to be <0.36 microg PPDeq/kg body weight/working day. Our results suggest that (a) current safety precautions for the handling of hair dyes offer sufficient protection against local and systemic exposure and (b) professional exposure to oxidative hair dyes does not pose a risk to human health.