Lead
in Hair - Concern Over its Use as an Indicator of Non-Occupational Exposure
By Prof Brian Gulson
Graduate School of the Environment, Macquarie University, Sydney
With increasing public awareness of lead as a health issue, The LEAD group has received
numerous calls regarding the availability and significance of lead measurements in hair
and nails, but especially hair. Concern over the toxic effects of environmental factors
such as heavy metals has also spawned an "Industry", promoting the use of trace
metals in hair.
I was recently approached by a subject who had his hair analysed, informed that the
lead was elevated and that he should undergo chelation therapy with EDTA. Brief details of
this case are as follows.
Subject A is a 27 year old student who had experienced for at least the past three
years symptoms which could be attributable to lead poisoning such as tiredness, sleep
disruptions, disinterest in studies, indigestion and facial flushing. Discussions with the
subject elicited no source 'of lead apart from the possibility of childhood exposure in
Germany from petrol, because of the proximity of his residence to a busy thoroughfare.
A naturopath had suggested hair analysis, the results of which were 6.1 ppm Pb and 86
ppm Cu. The interpretation of the results was that both metal concentrations were high and
it was recommended by a medical practitioner that the subject undergo chelation therapy
with EDTA, with no follow-up or even a blood lead analysis! Hair analyses are
not considered reliable indicators of lead exposure, as discussed below.
He agreed to a blood lead analysis prior to chelation. Blood lead analyses - despite
the drawbacks associated with a single analysis - are accepted internationally as the main
indicator of lead exposure. Duplicate analyses of a blood sample using the stringent CSIRO
protocol, showed it to contain 5.6 µg/dL, half the June 1993 NHMRC recommended goal for
all Australians. Furthermore, the lead isotopic fingerprint indicated a source of
Australian lead, not from Germany, although given that the subject has spent the past 22
years in Australia, it was highly unlikely that German lead would be detectable.
It is medically irresponsible for this subject to undergo chelation therapy with EDTA
given:
(i) the internationally accepted indicator of lead exposure, blood lead, was not measured,
(ii) the potential side effects of EDTA chelation, including depletion of essential
elements such as Zn, Fe and Cu, and even mobilisation of lead from skeletal sources (CDC
1991; Mann and Travers, 1991).
Status of Hair Analysis
Lead measurements in hair are not considered reliable indicators for exposure because
of the difficulty to distinguish what is in the hair from what is on it. These problems
arise form:
(i) the ease of external contamination (from air and dust, hair preparations (Fergusson,
1990; see table below)] because of the waxy nature of hair, and
(ii) the difficulty in decontaminating hair prior to analysis.
The CDC document (1991 page 55) states: "The following tests are
NOT indicated for the diagnosis or clinical management of lead poisoning:
Tests of Hair and Fingernails for Lead Levels."
After a thorough study of the literature, Taylor (1986) came to the
following conclusions, summarised by internationally regarded experts, Ewers and Brockhaus
(1991):
- Modern analytical procedures enable sensitive, accurate, and precise measurements of
trace element concentrations in human hair. Since inter-laboratory comparisons indicate
that the results are not always reliable, hair reference materials should be used
throughout the analytical process to ensure accurate analytical data. As far as I
know, no international reference materials are available.
- The interpretation of the analytical data represents a complex problem since trace
element concentrations of human hair are influenced by numerous factors including age and
sex of the subject, colour and growth site. Therefore, it is vital that reference levels
should be selected carefully so that these factors are taken into consideration.
Unfortunately, much of the experimental and investigative work have failed to do so, and
many studies are of doubtful validity. In addition, the contribution of external
contamination of the trace element content of hair is very variable, and it is difficult
or even impossible to control this factor.
- Even where it has been possible to control for these influences the most reliable
experimental data indicate that the trace element content of hair does not correlate
with the trace element concentrations in metabolically important tissues. Such large
and variable discrepancies were found that it is difficult to accept how the elemental
concentrations in hair could reflect the trace element status of a subject. Those
occasions in which the concentration of trace elements in hair can be shown to reflect
either body status or exposure are essentially extreme situations, usually with
significantly increased concentrations and evidence of toxicity. In these situations
parameters other than hair concentrations are more informative.
- With few exceptions mentioned above trace element analysis of hair is not a useful
procedure, in many instances it provides data that may be misleading. The activities of
laboratories which advertise and provide such analyses on a commercial basis can only be
viewed with scepticism
The concerns expressed above for many trace elements is exacerbated in
the case of lead because of its ubiquity.
A table of hair lead analyses from Fergusson (1990; Table 13.4, page
478; references included) also illustrates the variability in lead concentrations (in
parts per million; ppm) and futility in the interpretation of data at low concentrations.
| Country |
Mean
(ppm) |
Range (ppm) |
Comments |
| Austria |
|
0.97-44.9 |
|
| Canada |
10.1 |
0.5-25 |
Rural |
| |
16.9 |
0.5-35 |
Urban |
| |
45.2 |
10-350 |
Near
smelter |
| |
7.7 |
|
Children,
exposed |
| |
4.9,
4.1 |
|
Children,
not exposed |
| |
12.0 |
|
Adults,
exposed |
| |
3.4,
5.3 |
|
Adults,
not exposed |
| Greenland |
5.96 |
|
|
| Japan |
3.4 |
|
|
| New
Zealand |
12.8 |
2.0-360 |
Levels
relate to occupation |
| |
|
1050-2410 |
Use
hair preparations |
| |
10.4 |
1.2-111 |
City
survey |
| |
363 |
124-1381 |
Lead
workers |
| |
67.0 |
7-313 |
Lead
workers families |
| U.S.A. |
16.2 |
|
Children |
| |
6.55 |
|
Adults |
| |
|
7.6-107.1 |
Inc.
exposure areas |
| |
13.4* |
21-100 |
Children |
| |
12.2* |
20-155 |
Adults |
| |
36 |
|
Maternal scalp hair |
| |
14 |
|
Maternal pubic hair |
| |
13 |
|
Neonatal hair |
| Others |
1.0 |
0.05-15.0 |
Near roots |
| |
|
3-70 |
|
| *Geometric mean |
Conclusion
If the community wishes to avail itself of the "metals in
hair" services, that is their prerogative. However, if as an outcome of these
services, recommendations are proposed which could potentially impact negatively on a
person's health with no amelioration of their problems, it is irresponsible for the
service providers to make these recommendations.
References
CDC (1991). Preventing Lead Poisoning in Young Children. U.S.
Department of Health and Human Services, Centers for Disease Control, Atlanta, Georgia.
Ewers U. and Brockhaus A. (1991). Metal concentrations in human body fluids and
tissues. In: Metals and their compounds in the environment. Occurrence, analysis and
biological relevance. Edited by E Merian. VCH Publishers Weinheim, Germany, 199 1, pages
207 - 220.
Fergusson JE (1990). The heavy elects: chemistry, environmental impact and health
effects. Pergamon Press, Oxford.
Mann K.V. and Travers J.D. (1991). Succimer, and oral lead chelator. Clinical Pharmacy,
10, 914 -922.
Taylor A. (1986). Usefulness of measurements of trace elements in hair. Ann.
Clin. Biochem. 23, 364-378
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