Skip directly to search Skip directly to A to Z list Skip directly to navigation Skip directly to site content Skip directly to page options

Summary Report Hair Analysis Panel Discussion Exploring The State Of The Science

Hair Analysis Panel Discussion: Section 3.3

Historical Document

This Web site is provided by the Agency for Toxic Substances and Disease Registry (ATSDR) ONLY as an historical reference for the public health community. It is no longer being maintained and the data it contains may no longer be current and/or accurate.

Section 3
3.3 Analytical Methods

The group noted that reliable analytical methodologies do exist to measure and verify the presence of various substances in hair. Several panelists specified methods currently used for hair analysis in their pre-meeting comments; throughout the meeting, they mentioned some of the methods' strengths and weaknesses, as well as their applicability. This section highlights the points made during the meeting, but should not be considered an exhaustive discussion of existing methodologies. The methods discussed include:

Cold Vapor Atomic Absorption (AA). It was noted that this is the preferred methodology for measuring methyl mercury.

Inductively Coupled Argon Plasma Mass Spectrometry (ICP-MS). ICP-MS has widespread use in commercial laboratories. It can be used to measure methyl mercury, but it is difficult to get reproducible calibrations (DP). With certain types of mass spectrometry, stable isotope studies can help show the incorporation rates of certain elements in hair, which may help to answer some of the toxicology questions. For example, a 20-day delay has been shown between the appearance of lead in blood and its appearance in hair (TC).

Inductively Coupled Argon Plasma Optical Emission Spectrometry (ICP-OES) or Inductively Coupled Argon Plasma Atomic Emission Spectrometry (ICP-AES). Of the commonly used methods, ICP-OES/AES is used the most (DP). This method makes it possible to generate a large amount of data on a large number of elements. It is a "quick and dirty" way of getting a global picture of the elemental composition of a hair sample.

It was noted that, historically, CDC used Jarrell Ash Model 1160 AtomComp (e.g., to generate the data cited in DiPietro et al. 1989). CDC presently uses a Jobin Yvon Ultima C (DP).

Neutron Activation Analysis (NAA). NAA has been used in forensics to measure trace elements in small quantities of hair. It can be used for segmental analysis of hair. Segmental analysis can reveal isolated elevations of contamination along the hair and provide information regarding the contamination of the length of the hair over time. Identifying patterns over time can help distinguish whether exposure is endogenous or exogenous (see also Section 4). These techniques are not widely commercially available, however (MK).

X-ray Fluorescence. This technique is amenable, nondestructive, and multi-element. It also has the advantage of measuring the mass of hair as well as the amount of the element present in that segment of hair (TC). Another panelist noted that the distribution of mercury in segments along the length of a single strand of hair may be determined by x-ray fluorescence.

Proton Induced X-ray Emission (PIXE) Spectrometry. This method was brought into play approximately 30 years ago. This method studies a cross section of hair, enabling identification of external versus internal contamination. This method has not been used very much because the instrument is expensive (TC). One panelist noted that single-strand analysis can be problematic if hair is in the non-growing phase (RB), although it was noted that this is not a problem if the sample is taken from the root (TC).

Another panelist commented on the variable success of the PIXE method. For example, differentiating internal and external arsenic may not always be that straightforward. In cases of internal uptake, peaks of arsenic on the external shaft of hair may be a consequence of appreciable cysteine residues and sulphydral groups. In cases of external contamination, washing procedures may lead to greater incorporation of external contamination into the shaft (MK).

Given the various methodologies that might be used, several panelists pointed out the importance of understanding the method and analytical equipment used when interpreting hair analysis results, noting that it is the laboratory's responsibility to clearly report the method used, quality assurance measures taken, any possible interferences, etc. Further, the data user should carefully consider this information when evaluating the results.

As stated by one panelist, it is easy to standardize measurements by using good standards and good laboratory practice (use of blanks, use of external verification) (DP). While the group recognized that valid methods exist, several panelists stressed that the challenge lies in the interpretation (see Section 4 of this report)


Next | Table of Contents

Top of Page

 
Contact Us:
  • Agency for Toxic Substances and Disease Registry
    4770 Buford Hwy NE
    Atlanta, GA 30341
  • 800-CDC-INFO
    (800-232-4636)
    TTY: (888) 232-6348
    Contact CDC-INFO
  • New Hours of Operation
    8am-8pm ET/Monday-Friday
    Closed Holidays
USA.gov: The U.S. Government's Official Web PortalDepartment of Health and Human Services
Agency for Toxic Substances and Disease Registry, 4770 Buford Hwy NE, Atlanta, GA 30341
Contact CDC: 800-232-4636 / TTY: 888-232-6348

A-Z Index

  1. A
  2. B
  3. C
  4. D
  5. E
  6. F
  7. G
  8. H
  9. I
  10. J
  11. K
  12. L
  13. M
  14. N
  15. O
  16. P
  17. Q
  18. R
  19. S
  20. T
  21. U
  22. V
  23. W
  24. X
  25. Y
  26. Z
  27. #