Health Effects Related to Beryllium Exposure
Beryllium and beryllium-containing materials can be used in a safe
manner under most circumstances, but may present health hazards when
used under conditions involving adverse exposure. The purpose of this
statement is to identify these health hazards and the exposure
conditions under which they may arise.
The recognized health effects of such adverse exposure to the various
types of beryllium-containing materials include skin disease as well as
acute and chronic lung disease. These adverse effects are not seen with
all beryllium materials, but will vary from material to material,
depending upon a number of factors, including the chemistry, solubility,
physical size, and concentration of the material. It is important,
therefore, to identify the specific adverse effects, if any, of the
particular form of beryllium materials involved. Some forms of beryllium
have produced tumors in selected species of animals. Despite the
response noted in animals, there is not generally accepted evidence that
beryllium is a human carcinogen. Although some studies purport to show
such a relationship, they remain controversial.
Skin Effects
Two types of skin reaction have been seen in individuals involved in
the manufacture of beryllium products. The first involves the
implantation of either beryllium oxide or metallic beryllium under the
skin. This material may be introduced through cuts, abrasions, or
contamination of open wounds. It then sets up a foreign body reaction
which will continue to fester until the material is removed. Removal may
involve careful cleansing or surgical removal in some cases. Once the
material is removed, the wound heals readily without lasting reaction.
The second skin reaction is an irritant or contact dermatitis or rash
which is associated with direct contact with the soluble salts of
beryllium (usually beryllium chloride, beryllium sulfate, or beryllium
fluoride, the most reactive of all). These forms of beryllium are
utilized only in the beryllium producer's refinery and extraction plants
or in research laboratories. This localized skin reaction to beryllium
presents no hazard for the users of beryllium, beryllia, or alloys of
beryllium.
Acute Lung Disease
No case of acute beryllium disease has been reported in the past
twenty five years. This disease entity was caused by exposure to large
concentrations (in the order of 100 micrograms) of soluble salts of
beryllium. Engineering controls, installed in beryllium refinery and
extraction plants where these compounds are utilized in the basic
beryllium production processes, have reduced the airborne concentrations
of these materials to a level low enough to prevent this disease.
Although an accidental exposure in such plants is still possible, the
probability is quite remote. Today, acute beryllium effects on the
respiratory system are a matter of historical interest only, and,
outside of the basic beryllium producer's plants, of no practical
significance.
Chronic Beryllium Disease
The most serious health effect of adverse exposure to beryllium is
Chromic Beryllium Disease (CBD), once called "berylliosis".
This is an allergic type of lung response resulting from inhaling
airborne concentrations of beryllium particulates in the form of dusts,
mists, or fumes. In order to contract this disease three conditions must
be present. These are:
An immunologically responsive individual. In layman's language,
one must be "allergic" to beryllium to develop the
disease. About three to five percent of the population appears to be
susceptible. Recent research suggests that this selectivity in CBD
may be due to the presence of a genetic predisposition in this
susceptible population. Further research, designed to shed
additional light on the role of genetics in the development of the
disease, is now underway.
Minimum particle size. Since CBD can be caused only by inhalation,
the beryllium particles must be of a respirable size. In order to
develop CBD, beryllium particles must be small enough (less than ten
microns to enter and be retained in the air sacs in the lower
portion of the lung. Particles larger than ten microns are filtered
out by the nose hair or trapped in the mouth or the lining of the
bronchial tube before reaching the air sacs of the lung. These
particles will be swallowed and then excreted through the
gastro-intestinal tract without ill effect.
Adequate concentration. A sufficient number of these minute,
respirable beryllium particles must enter the lung to induce an
immunological reaction. This threshold level, below which no
reaction occurs, may vary from one susceptible individual to
another. Accordingly, airborne concentrations of beryllium should be
kept as low as possible. The OSHA standard intended to address CBD
is an average concentration over an eight hour day not to exceed two
micrograms of beryllium per cubic meter of air measured. Thus, in
any event, airborne concentrations of beryllium should never be
permitted to exceed the approved standard.
SUMMARY
There is no known skin hazard connected with touching or handling
solid forms of beryllium oxide, metallic beryllium or
beryllium-containing alloys. Beryllium is not radioactive and thus
presents no radiation hazard. There is no known hazard connected with
the ingestion of beryllium. The hazard associated with CBD is due
exclusively with inhalation.
CANCER
The question of whether occupational exposure to beryllium causes
cancer has been examined extensively for the past three decades without
producing any study that would demonstrate that beryllium exposure
causes human cancer.
The most recent and most extensive human study involved over 9,000
workers employed in the beryllium industry between 1940 and 1969 at
seven different plants. The two oldest plants, which operated in the
1940's, had no engineering controls in that period and workers were
exposed to massive levels of airborne beryllium. The remaining five
plants had varying degrees of engineering controls over the years and,
therefore, a lower level of air-borne beryllium. Workers in these five
plants showed fewer lung cancers than would be expected in a comparable
population, whereas workers in the two oldest plants showed a slightly
larger number than would be expected. When the authors of the study
adjusted for smoking, this excess was reduced to a level only slightly
above expected, a level of excess comparable to that seen in passive
smokers.
There are three plausible explanations for these results, but none is
more than an educated guess. The first explanation would be pure chance.
Having five points falling just below the mean and two falling just
above would fit a random probability pattern, with the age and condition
of the plants being pure coincidence. A second explanation would be that
beryllium is a weak carcinogen at the massive doses level seen in the
two oldest plants ( a thousandfold higher than current occupational
exposure levels), but at today's exposure levels, it is not an effective
carcinogen. The third explanation is smoking. Critics of the study
contend that the smoking adjustment made by the authors of the study was
inadequate and that when the date are properly adjusted for factors
unrelated to beryllium, such as smoking, all excess disappears, even in
the two oldest plants.
Regardless of the explanation selected, the plain fact is that there
is not evidence that the thousands of beryllium workers in the industry
today have any excess risk of cancer when compared to the general
population.
REFERENCE
"Beryllium Biomedical and Environmental Aspects", ed.
Rossman, M.D., Williams & Williams, Baltimore, 1991.
This information applies to a specific manufacturing operation. If
you need additional information on safe handling practices or technical
data on beryllium products, contact Instrument Specialties Delaware Water Gap P.O. Box 650, Shielding Way Delaware Water Gap, PA 18327 Tel: +1.570.424.8510 Fax: +1.570.424.6213
All material presented courtesy of
Brush Wellman, Inc., Cleveland, Ohio and
Instrument Specialties Company Inc., Delaware Water Gap, PA.
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