Hair Metal Levels Research Articles

A Comparative Study Based on Gender and Age Dependence of Selected Metals in Scalp Hair

Levels of 10 metals (Ca, Mg, Fe, Zn, Cu, Mn, Cd, Co, Cr and Ni) in the scalp hair of male and female donors, with age groups between 3 and 100 years, were determined by ICP-AES. In total, 58 male and 30 female hair samples were analyzed in triplicate. The donors belonged to the rural area of district Chakwal, a well-known typical non-urban site in Pakistan. Calcium showed the highest concentration of 462 microg/g in the hair of males and 870 microg/g in those of females followed by Zn, at 208 and 251 microg/g for the two sexes. For male donors, Cd showed the lowest concentration (1.15 microg/g) while for female donors Co remained at minimum level (0.92 microg/g). The order of decreasing metal concentration in the hair of male donors was: Ca > Zn > Mg > Fe > Cu > Mn > Ni > Cr > Co > Cd while that for female donors it was: Ca > Zn > Mg > Fe > Cu > Mn > Cr > Ni > Cd > Co. The female group exhibited enhanced levels of all selected metals except Fe and Co in their hair as compared with the male counterparts. A strong bivariate positive correlation was found between Fe and Zn (r = 0.841) for the hair samples from male category while for the female category, strong positive correlations were observed between Ca-Mg (r = 0.617), Ca-Zn (r = 0.569), Ca-Mn (r = 0.565), Mg-Mn (r = 0.655), Cr-Cu (r = 0.655) and Cr-Ni (r = 0.685). The distribution of metals in the hair of donors with respect to different age groups was also investigated for both genders. The study showed that in case of males, the concentration of all selected metals decreased with increasing age except for Cu, Co and Cr. However, for females the hair metal levels increased with age, except for Co for which the concentration decreased with age. No appreciable change in the metal concentration was observed as a function of age for the combined sexes.

Monitoring Metals in the Population Living in the Vicinity of a Hazardous Waste Incinerator: Levels in Hair of School Children

Hair samples of 134 school children (12-14 yr old) living in three residential zones in the vicinity of a new hazardous waste incinerator (HWI) (Constanti, Tarragona County, Catalonia, Spain) were analyzed by inductively coupled plasma-mass spectrometry (ICP-MS) for arsenic (As), beryllium (Be), cadmium (Cd), chromium (Cr), mercury (Hg), manganese (Mn), nickel (Ni), lead (Pb), tin (Sn), thallium (Tl), and vanadium (V) concentrations. These concentrations were compared with those obtained in a baseline survey performed in the same area during the period of construction of the HWI. Current mean concentrations ranged from values under the respective limit of detection (As, Be, Cd, Tl, and V) to 0.70 and 0.86 microg/g for Hg and Pb, respectively. In comparison to the baseline survey, the levels of Cr, Mn, Ni, Pb, and Sn showed a significant reduction, whereas Hg concentrations were similar. No significant differences were observed according to the sex of the children. However, some differences were noted, especially for Pb and Cr, with respect to the specific zone of residence. In general terms, the current metal levels in hair of school children are similar or even lower than those recently reported for a number of industrial and residential areas of various regions and countries.

Metal Concentrations in Hair and Cognitive Assessment in an Adolescent Population

The objective of this study was to establish the potential relationship between the levels of various metals in hair and cognitive functions in children living in zones of Tarragona (Catalonia, Spain) with different metal pollution levels. Thirty-nine boys and 61 girls (12-14 yr old) from various schools were selected for the study. The concentrations of cadmium (Cd), chromium (Cr), mercury (Hg), lead (Pb), manganese (Mn), nickel (Ni), and tin (Sn) in scalp hair were determined by inductively coupled plasma- mass spectrometry (ICP-MS). Attention, visuospatial capabilities, and abstract reasoning were assessed as indicators of cognitive impairment. Three categories of attention were defined: low, medium, and high. A significant negative correlation (p=0.019) between Pb levels in hair and attention was observed. Significant differences between Pb levels in hair in low- and medium-performance groups and those in the high-performance group were also found. Moreover, a positive correlation (p=0.048) between Hg hair concentrations and visuospatial capabilities was also noted.

Development of an analytical method for monitoring worker populations exposed to platinum-group elements

The increasing industrial use of platinum-group elements (PGEs), namely Ir, Pd, Pt and Rh, and related allergies such as rhinitis, conjunctivitis, asthma, urticaria and contact dermatitis, have led to a growing need to monitor selected populations of exposed workers. In this study, the levels of PGEs were measured in indoor airborne particulate matter and in biological samples taken from employees of a plant where car catalytic converters are produced and precious metals are recovered from spent carbon catalysts. The development of an analytical procedure based on quadrupole inductively coupled plasma mass spectrometry (Q-ICP-MS) for the analysis of PGEs in airborne particulate matter and on sector field inductively coupled plasma mass spectrometry (SF-ICP-MS) for the analysis of PGEs in blood, serum, urine and hair is described. For airborne particulate matter deposited on filters, the limits of detection (LoDs) were found to be 0.006 ng m −3, 0.020 ng m −3, 0.018 ng m −3 and 0.006 ng m −3 for Ir, Pd, Pt and Rh, respectively. Repeatability of measurements ranged from 1.8 to 8.5%, while recovery was in the range from 92 to 102%. For biological samples LoDs in blood, serum, urine and hair ranged from (in ng l −1) 0.2–0.6 for Ir, 5–10 for Pd, 1–3 for Pt and 2–3 for Rh. For all biological materials, the repeatability varied from 1.1 to 12% for the four elements. Recovery data for the determination of PGEs in biological matrices were found to range from 84.0 to 107.8%. The method was applied to the determination of either total or respirable airborne PGEs collected from five different work areas in the plant. The difference between areas with high and low exposure correlates closely with metal levels in hair, blood and urine. The correlation coefficients between Pt in airborne particulate matter and Pt in biological materials was 0.994, 0.991 and 0.970 for blood, hair and urine, respectively.

Mercury concentrations in hair exposed in vitro to mercury vapor.

Hair is often used as an index of environmental and industrial exposure to different metals. The interpretation of metal levels in hair is difficult because of the risk of external contamination. The aim of this study was to define the degree of external contamination of hair exposed in vitro to mercury vapor. Specimens of hair were exposed to concentration: 0.026, 0.21, and 2.7 mg Hg/m3 for 2-28 d. Mercury levels in hair increased during 28 d of exposure 2, 3 and 13, times, respectively, when compared to initial values. Mercury levels in hair exposed to the first and second (but not third) concentration of mercury vapor attained a steady state on the 21st d of exposure. The contamination of hair with mercury could not be removed by washing with water, solvent, and detergent. Hair may be used as an index of internal uptake of mercury provided that it was not externally exposed to mercury vapor. In cases of occupational exposure to mercury vapor, hair could become a useful tool for monitoring exposures.

Monitoring of cadmium, copper, lead and zinc status in young children using toenails: comparison with scalp hair

Cadmium, copper, lead and zinc concentrations were determined (atomic absorption spectrometry) in the proximal end of scalp hair ( n = 474) and in toenail clippings ( n = 461) of children, aged 3–7 years, living in an industrialized and in a rural area of the Federal Republic of Germany. With the exception of Zn in hair, levels of the elements were log-normally distributed. Data are presented as geometric means. Toenail Cd and Pb levels were much higher than those in hair (Cd, 457 vs 90 ng g −1; Pb, 8.5 vs 2.7 μg g −1), while Cu and Zn values were similar in both biological media (toenail vs hair: Cu, 7.5 vs 10.6 μg g −1; Zn, 129 vs 108 μg g −1). In toenails, all elements were positively correlated with each other. In hair, there was a close relationship only between Cd and Pb; Cd and Pb were inversely related to Zn. With the exception of Zn (no correlation), there was a minor relationship between metal levels in hair and those in toenails. Using stepwise regression analysis, seasonal variation was found to be the main factor influencing hair metal levels, while nail metal levels were mainly influenced by place of residence (with the exception of Cu concentrations, for which there were no significant predictors). Multiple correlation coefficient was higher for hair than for nails. It is concluded that, for biological monitoring, toenail clippings are less suitable than hair samples.

Cadmium, copper, lead, and zinc concentrations in human scalp and pubic hair

Cadmium, Cu, Pb, and Zn concentrations were measured in the first 3 cm of the proximal end of scalp hair and in pubic hair of 41 humans, by atomic absorption spectrometry. Data are presented as geometric means. Scalp hair (SH) metal levels were higher than those in pubic hair (PH), (Cd, 85.1 vs 60.8 ng g −1; Cu17.7 vs 11.9 μg g −1; Pb, 1.72 vs 1.05 μg g −1; Zb, 148.8 vs 133.3 μg g t1̄) with correlation coefficients of: Cd, r = 0.474; Cu, r = 0.549; Pb, r = 0.576; and Zn, r = 0.263. Further correlations were established between Cd and Pb levels (SH, r = 0.691; PH, r = 0.621) as well as between Cd and Zn levels (SH, r = −0.268). In PH the Cd, Cu, and Pb levels of males were higher than those of females, whereas the Zn levels were lower in SH and PH of males. Scalp hair Zn contents were inversely related to age. Cadmium and Pb levels in SH and PH were higher in summer than in winter, whereas the SH Zn contents were higher in winter. An influence of place of residence, smoking habit, hair colour and hair structure on SH and PH metal levels is identified. It is concluded that hair metal analysis in samples close to the scalp is not seriously invalidated by sources of external contamination.

Uptake of Aluminum, Cadmium, Copper, Lead, and Zinc by Human Scalp Hair and Elution of the Adsorbed Metals

Uptake of aluminum (Al), cadmium (Cd), copper (Cu), lead (Pb), and zinc (Zn) from aqueous solutions by human scalp hair (water/hair = 100:1) has been studied in the concentration range 0-50 mg/L. Hair metal levels were determined by a wet digestion procedure and atomic absorption spectrometry. Under conditions used, uptake followed a sigmoid concentration-response relationship. The order of binding capacity of hair to the metals was as follows: Al greater than Cd greater than Cu greater than Pb greater than Zn. Using logit transformation 50% saturation was evaluated at the following metal concentrations (hair metal concentration of saturation is given in parenthesis): 0.34 mg/L for Al (0.154 mg/g); 1.82 mg/L for Cd (0.363 mg/g); 2.21 mg/L for Cu (0.651 mg/g); 2.52 mg/L for Pb (0.986 mg/g); 23.84 mg/L for Zn (1.616 mg/g). Percentage elution of trace metals from hair after treatment with metal-enriched solutions by five different procedures ranged from 14.5 to 46.5% for Al, from 11.1 to 28.9% for Zn, from 11.5 to 28.4% for Pb, from 8.9 to 13.6% for Cd, and from 0.1 to 11.8% for Cu. In addition, trace element concentrations were measured in tap water samples and shampoos.

Correlation clusters in the accumulation of metals in human scalp hair: effects of age, community of residence, and abundances of metals in air and water supplies

Scalp hair samples taken from 122 children and 27 adults from three native Indian villages in northern Alberta, Canada were analyzed for 32 metals, in an attempt to tract industrial pollution into the human population. One of the villages has been exposed since 1967 to increased levels of several metals due to its proximity to the world's first two oil sands petroleum extraction plants (Suncor and Syncrude), which release large amounts of metals into the environment. Metal-enriched particulates are emitted at a rate of 547–780 kg h −1 for Suncor, and 713–1067 kg h −1 for Syncrude. To test the hypothesis that hair content reflected accumulation of environmental metals, water and aerometric samples were collected and analyzed for their metal content. These analyses demonstrated that elevated levels of nine metals in hair from children in one of the control villages (Garden River) are (with the exception of Al) correlated with increased levels of metals in water and air. Moreover, increased levels of Cu, but lowest levels of all other metals were found in hair and environmental samples from one control village (Fort Chipewyan). Correlation matrices for metals in the hair samples revealed three sets of highly intercorrelated metals (‘correlation clusters’): (i) Pb/Cd; (ii) Al/V/Fe; (iii) Ca/Mg/Sr/Ba. These groups of metals were significantly intercorrelated ( r > 0.6, p < 0.001) in the total population, and in both children and adults, or both males and females, as well as when the population was compared according to community of residence. The robustness of the clusters is particularly noteworthy in view of large differences in the proportions and absolute amounts of the various metals in hair from children in the three villages. Plots of metal levels in hair as a function of age of subject reveal a dramatic decrease in concentrations of Al, V, and Fe during the first years of life. The high levels of Al and V in hair from very young children may reveal a lower selectivity in metal absorption, and a higher risk of toxicity during a period of rapid growth when need for nutritionally essential metals is particularly high.

Trace metals in scalp hair of children and adults in three Alberta indian villages

This study examined trace metal levels in scalp hair taken from 122 children and 27 adult residents of three small northern Alberta (Canada) Indian villages, one of which is situated close to the world's first tar sands oil extraction plants. The three communities studied were: Fort McKay (the exposed village), Fort Chipewyan (also in the tar sands ecosystem but distant from the plants), and Garden River (not in the tar sands ecosystem). Inductively coupled argon plasma emission spectroscopy was used to determine hair sample metal content. Nineteen metals were included in data analysis. Children from Fort McKay had the highest average hair lead, cadmium and nickel levels. Chromium levels were approximately equal in hair from Fort McKay and Garden River children, and significantly elevated above levels found in the hair of Fort Chipewyan children. Children from Garden River showed highest hair levels of eight metals: vanadium, aluminum, iron, manganese, barium, zinc, magnesium and calcium. Fort Chipewyan children had the highest hair levels of copper, but the lowest levels of all other metals. Among adults, hair lead, nickel and cadmium levels were highest in Fort McKay residents, while phosphorous and vanadium were highest in hair from Garden River residents. Bioaccumulation of lead, cadmium, nickel and chromium in hair from Fort McKay residents may be related to exposure to extraction plant pollution. Plant stack emissions are known to contain appreciable amounts of lead, nickel and chromium. Spills into the Athabasca River, until recently the source of Fort McKay drinking water, have been reported from plant wastewater holding ponds, known to contain elevated levels of lead, nickel and cadmium. An increased number of significant metal—metal correlations in hair metal levels for Fort McKay children suggests a richer source of multiple metal exposure, relative to children in the other two communities.

Levels of metals in hair of young children as an indicator of environmental pollution

In 1982 the levels of lead (Pb), cadmium (Cd), vanadium (V), copper (Cu), and selenium (Se) were determined in hair of 231 four- to five-year-old children. The objective was to explore the feasibility of using metal-in-hair levels in groups of children as an indicator of environmental pollution. The study was carried out in four areas, which were assumed to differ in ambient pollution by metals. A questionnaire on personal data, socioeconomic status, intake of beverages, and life-style was completed by the parents. The metal-in-hair levels covered a large range. The variables pertaining to location together with sex, presence of a garden, and drinking of coffee and/or tea explained 32% of the variance of Pb, 24% of the variance of Cd, and 21% of the variance of V. The total variance explained by all measured questionnaire items was at best 38%. The location was the most important factor. Cu and Se levels did not differ between the locations.

Heavy metal exposure in populations living around zinc and copper smelters.

Arsenic, cadmium, and lead levels were determined simultaneously in multiple environmental media and human tissues in two zinc smelter (Bartlesville, Oklahoma and Palmerton, Pennsylvania) and two copper smelter (Ajo, Arizona and Anaconda, Montana) communities. Environmental media sampled included air, soil, household dust, and tap water; human samples included hair, blood, and urine. Between 200 and 300 residents from various age groups (1-5, 6-18, 20-40, and 60 + yr) were sampled in 1978 and 1979 and completed questionnaires in each of the four communities. Samples for all media were selected under a probability sampling framework at various distances from the smelters. Results of this investigation indicated that increased environmental levels and body burdens were exhibited at distances closest to the smelters. Of the three tissues sampled, hair was the most useful in determining relationships between environmental metal levels, distance, and body burden. Furthermore, while there was evidence that all ages had hair metal levels that were related to environmental levels and distance from the smelter, these relationships were much more pronounced for the 1- to 5-yr-old age group. The 1 to 5 yr olds also had the highest tissue metal levels across age groups. Higher hair metal levels were also found for males; smokers; children who ate paint, dirt, or clay; and for individuals who spent more time out of doors.

Zinc, copper, iron and lead in scalp hair of students and non-student adults in Oxford.

Scalp hair samples contributed by 215 students and non-student adults in Oxford were washed, ashed and analysed by atomic absorption spectrophotometry for zinc, iron, copper and lead. The overall results were within the ranges reported from similar investigations carried out elsewhere and are what might be expected with normal, healthy subjects. However, examination of the results for different groups showed some significant differences between levels of the nutrient metals in student and non-student hair. Results for lead indicate a low level of environmental contamination for all subjects.

Editorial: Hair analysis: what does it tell us?

In selected applications in forensic, clinical, or epidemiologic medicine, trace-metal hair analysis, along with other tests, is a useful tool. Nevertheless, present scientific knowledge does not support the use of metal levels in hair for broad, sophisticated, subtle diagnostic purposes (such as vitamin deficiencies, enzyme activity, and allergic states), and certainly, hair analysis is not desirable for routine use. The state of health of the body may be entirely unrelated to the physical and chemical condition of the hair. Hair can be mechanically damaged by rough drying procedures, brushing, combing, or pulling (as in the use of rollers). Chemically, hair can be altered during waving, straightening, dyeing, and bleaching; moreover, products such as tonics, hair sprays, conditioning or grooming aids, or shampoos also influence the condition of the hair; lead, zinc, and selenium are deposited on the hair after the use of some of these preparations. There are not only