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Revisited digestion methods for trace element analysis in human hair

Abstract

Background

The human hair is a potential material for assessing the exposure to environmental contaminants and tracing human mobility. Although various digestion methods have been proposed for determining trace elements in the human hair, there is no consensus about the best method among them yet.

Findings

We examined five different methods in order to determine the best method yielding the most accurate and precise data of trace elements in the human hair using two certified reference human hairs (IAEA085 and IAEA086) under controlled conditions (temperature, the volume of hydrogen peroxide (H2O2), and the number of digestion). Results showed that a high temperature of 160 °C yields better recovery rates than a low temperature of 70 °C. Furthermore, the additional input of H2O2 increases the recovery rate from 90 to 102%, and the two-time digestion also promotes the recovery rate.

Conclusions

This study suggests that although the combination of high temperature (160 °C), high volume of H2O2 (0.4 mL), and two-time digestion yields the most accurate and precise data of trace elements in the human hair, the digestion method should be carefully selected depending on the content of organometallic cation.

Introduction

The human hair is mostly composed of keratin (50% C, 21% N, 17.5% H, 6.5% O, and 5% S) with a small amount of trace elements, such as Ca, Fe, K, Na, and Sr (Font et al. 2012). Because trace elements are incorporated into the hair through diet and environmental exposure (Dongarrà et al. 2011), the determination of them can allow us to infer environment where a human was exposed during his or her life. For example, farmer’s hairs informed the prolonged exposure to pesticides and fertilizers (Hamid et al. 2017). Furthermore, Varrica et al. (2014) showed that hairs of children who were grown at the contaminated area by abandoned mines yielded high concentrations of heavy metals. For these reasons, the human hair has been commonly used in forensic science and archaeology (Kempson et al. 2010; Pragst et al. 2017).

In this context, the critical issue is to accurately and precisely determine trace elements in the human hair. Many studies have commonly used a digestion method using a mixture of ~ 0.8 mL of nitric acid (HNO3) and 0.2 mL of hydrogen peroxide (H2O2) to measure trace elements in the human hair and nail (e.g., Luo et al. 2014; Ishak et al. 2015), while experimental conditions, such as temperature (T), digestion duration, and apparatus, are slightly different from each other. For example, hair samples were reacted with a mixture of 1 mL of HNO3 and 0.1 mL of H2O2 in an ultrasonic cleaner at T = 75 °C during 60 min (Barbieri et al. 2011). Tipple et al. (2018) digested hair samples using a microwave digestion system at T = 200 °C (13.3 °C/min rate) during 30 min, while Font et al. (2012) used a mixture of 1.5 mL of HNO3 and 0.5 mL of HCl at T = 110 °C for 24 h, and then a mixture of 0.1 mL of HNO3 and 0.1 mL of H2O2 at T = 105 °C for 10 min. Nonetheless, there is no standardized digestion method yet until now. Here, we examined five different digestion methods using two certified hair standards (IAEA085 and IAEA086) and compared them regarding the recovery rates relative to certified values. This study will provide a guideline for the human hair digestion.

Materials and methods

Sample

Two certified hair standards (IAEA085 and IAEA086; human hair) were used in this study, of which the former represents hair with an elevated level of methylmercury (MeHg+; CH3Hg+), while the latter is representative of the endogenous level for MeHg+. The samples were cryogenically homogenized using the stainless steel “CryoPalla” mill at the KFA-Jülich Specimen Bank facility, until approximately 70% of the samples have a particle size below 71 μm. Then, the samples were γ-sterilized to ensure long-term stability of the material by inhibiting microbial action (IAEA, 2019a and 2019b).

Pre-cleaning

In order to remove possible contaminants, samples were cleaned using a 0.5% Triton X-100 (Sigma Aldrich), washed several times using a ACS grade acetone (Honeywell B & J), and finally washed three times using a MilliQ water following the procedures in Borella et al. (1996). Then, the pre-cleaned samples were completely dried in an oven at T = 60 °C.

Digestion

Pre-cleaned hair samples were digested using five different methods, in which the volume of reagent, reaction temperature, and the number of digestions were controlled (Fig. 1). Furthermore, both IAEA085 and IAEA086 samples were prepared in duplicate using method 3 in order to quantify analytical uncertainty.

Fig. 1
figure 1

Flow chart showing digestion procedures for five different digestion methods

First digestion

About 0.2 g of pre-cleaned hair samples were put in 60 mL Teflon vessels, and then, 5 mL of ultrapure HNO3 was added. One sample was heated on a hot plate at T = 70 °C overnight (method 1), and the others were at T = 160 °C (methods 2 and 3). In order to investigate the effect of H2O2 on recovery rates, either 0.2 mL or 0.4 mL of H2O2 was added to the samples (methods 1 and 2, and method 3, respectively) and reacted for 30 min. The samples were dried and re-dissolved in 10 mL of 5% HNO3.

Second digestion

Two aliquots from methods 1 and 2 were dried and then additionally reacted with 10 mL of ultrapure HNO3 in Teflon vessels. Each sample was digested on a hot plate at T = 70 °C (method 4) and 160 °C (method 5) for 8 h. Then, the samples were dried and re-dissolved in 10 mL of 5% HNO3.

Elemental analyses

Concentrations of trace elements (Ca, Cu, Mg, Mn, Sr, Zn) were measured using a PerkinElmer Optima 8300 ICP-AES at the Korea Basic Science Institute (KBSI). Repeated analyses of two certified standards (Trace Metals in Drinking Water, TMDW; and river water for trace metals and other constituents, SLRS-6) yielded analytical accuracy better than ± 5%. Furthermore, the analytical uncertainty for both IAEA085 and IAEA086 samples was less than 4% for all elements, ranging from 0.1 to 0.9% and from 0.8 to 3.6%, respectively (Table 1).

Table 1 Trace elements in two certified reference human hairs (IAEA085 and IAEA086)

Results and discussion

Table 1 presents measured and certified values of trace elements (Ca, Cu, Mg, Mn, Sr, Zn) for IAEA085 and IAEA086.

Effect of temperature: methods 1 versus 2

Most of the samples prepared by first digestion showed the recovery rate of approximately 73 to 96% for all trace elements (Table 1; Fig. 2a). Between T = 70 and 160 °C, a high temperature yielded much better recovery rates than a low temperature in both IAEA085 and IAEA086 samples (see Table 1; IAEA085-70 and IAEA086-70) although both methods display much less than 100% of recovery rate. For example, the recovery rates of Ca (84%), Cu (88%), Mg (80%), Mn (89%), and Zn (96%) in IAEA086-160 were slightly higher than those in IAEA086-70: Ca (79%), Cu (86%), Mg (79%), Mn (87%), and Zn (95%). During the experiment, after digestion with HNO3 at T = 70 °C, the final solution showed dark pale yellow, whereas the high temperature showed bright pale yellow. This result indicated that a high temperature allowed organic materials in hair samples to efficiently decomposed, and therefore yielded higher recovery rates.

Fig. 2
figure 2

Bar charts showing the recovery rates of trace elements obtained from five different digestion methods; Effects of temperature (a), H2O2 (b), and number of digestion (c) and (d).The recovery rate was calculated by dividing measured value by certified value. Both IAEA085 and IAEA086 samples were prepared in duplicate using the method 3

Effect of H2O2: methods 2 versus 3

In order to promote the recovery rate and examine the effect of H2O2, we added different volume of H2O2 during the digestion at T = 160 °C. The result showed that a high volume of H2O2 (0.4 mL) enhanced the decomposition of organic materials yielding high recovery rate compared to a low volume of H2O2 (0.2 mL). For example, IAEA085-160 method yielded the recovery rates of 88% for Ca, 86% for Cu, 91% for Mg, 79% for Mn, and 78% for Zn, while IAEA085-160HP showed better recovery rates of > 90% in all trace elements: 91% for Ca, 91% for Cu, 90% for Mg, 98% for Mn, and 97% for Zn (Fig. 2b). The similar results were observed in the IAEA086 sample (IAEA086-160 and IAEA086-160HP; Table 1), but the effect of H2O2 is much clearer in the IAEA086 sample. It could be due to the difference of MeHg+ content in the IAEA085 (22.9 mg/kg; IAEA, 2019a) and IAEA086 (0.258 mg/kg; IAEA, 2019b) samples, causing inefficient decomposition of high organometallic cation in IAEA085 although the same volume of H2O2 was added. The amount of samples used in this experiment is much more than the recommended sample size for inorganic analyses (> 10 mg) (IAEA, 2019a and 2019b), deteriorating complete decomposition of organic compounds, especially for IAEA085 with higher MeHg+ content (22.9 mg/kg). Organic compounds in hair samples may be incompletely oxidized during the digestion using even a microwave oven, causing inaccurate analytical result (Novozamsky et al. 1995; Almeida et al. 1999). In short, our results indicated that the more volume of H2O2, the better recovery rate of trace elements in hair samples.

Effect of number of digestion: methods 1 versus 4, and 2 versus 5

Two digested samples, IAEA085 (or 086)-70 and IAEA085 (or 086)-160, were digested again at T = 70 °C and 160 °C (IAEA085 (or 086)-70S and IAEA085 (or 086)-160S, respectively) in order to examine the effect of the number of digestion on trace element analysis. As shown above, the results showed that high temperature yielded better recovery rates for all analyzed elements. Furthermore, two-time digestion greatly enhanced the recovery rate of Zn (up to 22%) in IAEA085-70S (method 4) compared to IAEA085-70 (method 1) (Table 1) but little differences in other elements (Fig. 2c). On the contrary, IAEA085 (or 086)-160S (method 5) showed much better recovery rates for all elements than IAEA085 (or 086)-160 (method 2), yielding the recovery rates of most element range between 91 and 103% (Fig. 2d). The effect of the number of digestion on the recovery rate is much remarkable in IAEA085, showing the recovery rates of 102% for Ca, 103% for Cu, 101% for Mg, 98% for Mn, and 110% for Zn (Fig. 2c, d; Table 1). The result indicated that samples containing high content of organometallic cation (IAEA085) should be digested twice at higher temperature (T = 160 °C) in order to efficiently decompose it. Overall, this study indicates that the combination of high temperature (T = 160 °C) and much volume of H2O2 (0.4 mL) is the best method (method 3) for digesting human hair having low content of organometallic cation (IAEA086), while that of high temperature (T = 160 °C), H2O2 (0.2 mL), and two-time digestion is the best one (method 5) for human hair containing high content of organometallic cation (IAEA085).

Conclusions

The best digestion methods for trace element analysis in the human hair were examined using two certified reference human hairs, IAEA085 and IAEA086, under controlled experimental conditions. The results showed that human hair containing high content of organometallic cation (MeHg+), IAEA085, was completely digested using the combination of high temperature (T = 160 °C), H2O2 (0.2 mL), and two-time digestion, while that with low content of organometallic cation (IAEA086) using the combination of high temperature (T = 160 °C) and much volume of H2O2 (0.4 mL). This study highlights that the combination of high temperature and several times digestions allows to better determine trace elements in the human hair containing a high content of organic compounds, but that the digestion method should be carefully selected with a consideration for the content of organometallic cation.

Availability of data and materials

Upon reasonable request, the datasets of this study can be available from the corresponding author (J.-S. Ryu, jongsikryu@pknu.ac.kr).

Abbreviations

ICP-AES:

Inductively coupled plasma atomic emission spectrometer

TMDW:

Trace metals in drinking water

References

  • Almeida AA, Jun X, Lima JLFC. Determination of transition metals in human hair by high-performance liquid chromatography using sodium hexadecane-sulfonate coated columns. Talanta. 1999;50:253–9.

    Article  CAS  Google Scholar 

  • Barbieri FL, Cournil A, Sarkis JES, Bénéfice E, Gardon J. Hair trace elements concentration to describe polymetallic mining waste exposure in Bolivian Altiplano. Biol Trace Elem Res. 2011;139:10–23.

    Article  CAS  Google Scholar 

  • Borella P, Rovesti S, Caselgrandi E, Bargellini A. Quality control in hair analysis: a systematic study on washing procedures for trace element determinations. Mikrochim Acta. 1996;123:271–80.

    Article  CAS  Google Scholar 

  • Dongarrà G, Lombardo M, Tamburo E, Varrica D, Cibella F, Cuttitta G. Concentration and reference interval of trace elements in human hair from students living in Palermo, Sicily (Italy). Environ Toxicol Pharmacol. 2011;32:27–34.

    Article  Google Scholar 

  • Font L, van der Peijl G, van Wetter I, Vroon P, van der Wagt B, Davies G. Strontium and lead isotope ratios in human hair: investigating a potential tool for determining recent human geographical movements. J Anal At Spectrom. 2012;27:719–32.

    Article  CAS  Google Scholar 

  • Hamid ZA, Ishak I, Lubis SH, Mohammad N, Othman H, Saat NZM, Ghazali AR, Rahim SZA, Noor MRM. Evaluation of trace elements in the nails and hair of farmers exposed to pesticides and fertilizers. J Agr Sci. 2017;9:79–88.

    Google Scholar 

  • IAEA (2019a) IAEA-085, Human Hair (Methyl Mercury). https://nucleus.iaea.org/rpst/ReferenceProducts/ReferenceMaterials/Trace_Elements_Methylmercury/IAEA-085.htm.

  • IAEA (2019b) IAEA-086, Human Hair (Methyl Mercury). https://nucleus.iaea.org/rpst/referenceproducts/ReferenceMaterials/Trace_Elements_Methylmercury/IAEA-086.htm.

  • Ishak I, Rosli FD, Mohamed J, Ismail MFM. Comparison of digestion methods for the determination of trace elements and heavy metals in human hair and nails. Malays J Med Sci. 2015;22:11–20.

    PubMed  PubMed Central  Google Scholar 

  • Kempson IM, Skinner WM, Martin RR. Changes in the metal content of human hair during diagenesis from 500 years, exposure to glacial and aqueous environments. Archaeometry. 2010;52:450–66.

    Article  CAS  Google Scholar 

  • Luo R, Zhuo X, Ma D. Determination of 33 elements in scalp hair samples from inhabitants of a mountain village of Tonglu city, China. Ecotox Environ Safe. 2014;104:215–9.

    Article  CAS  Google Scholar 

  • Novozamsky I, van der Lee HJ, Houba VJG. Sample digestion procedures for trace element determination. Mikrochim Acta. 1995;119:183–9.

    Article  CAS  Google Scholar 

  • Pragst F, Stieglitz K, Runge H, Runow K-D, Quig D, Osborne R, Runge C, Ariki J. High concentrations of lead and barium in hair of the rural population caused by water pollution in the Thar Jath oilfields in South Sudan. Forensic Sci Int. 2017;274:99–106.

    Article  CAS  Google Scholar 

  • Tipple BJ, Valenzuela LO, Ehleringer JR. Strontium isotope ratios of human hair record intra-city variations in tap water source. Sci Rep. 2018;8:3334.

    Article  Google Scholar 

  • Varrica D, Tamburo E, Milia N, Vallascas E, Cortimiglia V, De Giudici G, Dongarrà G, Sanna E, Monna F, Losno R. Metals and metalloids in hair samples of children living near the abandoned mine sites of Sulcis-Inglesiente (Sardinia, Italy). Environ Res. 2014;134:366–74.

    Article  CAS  Google Scholar 

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Acknowledgements

The authors thank K. Kim and M.-J. Jung for sample preparation.

Funding

This project was supported by the KBSI grant (C39730).

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Contributions

J-SR and W-JS designed the study and led the writing of the manuscript. MJ conducted sample preparation and chemical analysis. All authors contributed equally to the data interpretation. All authors read and approved the final manuscript.

Authors’ information

Jong-Sik Ryu was a professor at the Graduate School of Analytical Science and Technology in Chungnam National University, and a principal researcher at the Research Center for Geochronology and Isotope Analysis in Korea Basic Science Institute when the work was designed and is now an assistant professor at the Department of Earth and Environmental Sciences in Pukyong National University. Phone: +82-51-6296624, FAX: +82-51-6296623, E-mail: jongsikryu@pknu.ac.kr

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Correspondence to Jong-Sik Ryu.

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Shin, WJ., Jung, M., Ryu, JS. et al. Revisited digestion methods for trace element analysis in human hair. J Anal Sci Technol 11, 1 (2020). https://doi.org/10.1186/s40543-019-0200-6

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