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Asbestos in Water
A hazard to health?
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i. Introduction inhalation of large quantities of airborne asbestos fiber
in occupational settings is known to increase the risk of respiratory disease and certain cancers among industrial, construction and shipyard workers. There is also an indica tion of increased incidence of gastrointestinal (Gl) cancer among such workers. These findings have led to specula tion that the general public is subject to a health risk from the asbestos fiber which can be found in water.
This pamphlet sorts out the different issues connected with the concern about asbestos and water, and presents the more recent comments of the U.S. and international public health community on this topic.
II. Sources of Asbestos in Water Asbestos is found in water supplies everywhere. The
three principal sources of the asbestos fibers are natural contamination from erosion of asbestos mineral deposits, effluent discharges from industry, and use of asbestos ce ment pipe water distribution systems.
In water, wide-ranging concentrations of asbestos have been reported. Concentrations in the U.S. in excess of 10 million fibers per liter are uncommon. Consistently, the highest water concentrations result from natural contamina tion. Raw waters, generally, contain higher concentrations of asbestos and those levels become reduced due to the normal water treatment given to drinking water supplies.
Most water samples taken in different surveys of 406 U.S. cities found less than one million fibers of all sizes per liter; about 10 percent between one and 10 million fibers; and, another 10 percent more than 10 million.1
Very exacting analysis, transmission electron microscopy coupled with selected area diffraction, is required to iden tify asbestos particles in water.
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ill. Asbestos Serves the World Asbestos fibers have long been used by man. Today,
asbestos has many important technological applications in our modern society.
Asbestos, a generic term, describes a number of natural ly occurring fibrous minerals located in various concen trations across the earth's surface. As generally recogniz ed, the term encompasses six minerals: chrysotile, amosite, crocidolite and fibrous forms of tremolite, anthophyllite and actinolite.
Asbestos has found its way into preferred use because
of its high tensile strength, superior flexibility and durability, favorable friction properties, and resistance to fire, heat and corrosion. This unique combination of properties remains unmatched by any other fiber, natural or man-made.
In recent times, certain asbestos uses have been phased out. Asbestos continues to be used in products in which the asbestos fibers can be "locked-in" by binders, such as cement, resins and plastics. Such products can be safely used without significant fiber release.
In 1986, U.S. consumption was 112,000 tons of asbestos. Estimates of world production total over four million tons, with the USSR and Canada continuing to be the leading miners.
IV. Asbestos Exposure and Gl Cancer Speculation and public concern has been frequently
voiced about the possible hazards from ingestion of asbestos fibers commonly found in drinking water. The con cern arises from the increased number of gastro-intestinal cancers (Gl) identified among persons exposed to airborne asbestos in some occupational settings. The large body of evidence now in existence is, however, generally agreed to support this assessment of asbestos in water: "the sug gested risks have never been conclusively confirmed, the issue very probably [is] a non-problem."2
One of the most important recent findings is that despite numerous animal feeding studies, at least a dozen which used a total of 10,000 animals with some being fed massive doses of asbestos, none indicates that ingested asbestos is carcinogenic.3 One of the several National Toxicology Program animal feeding studies reported in 1984, was in terpreted by NTP as showing "some evidence" of car cinogenicity in exposed male rats. However, the U.S. En vironment* Protection Agency's Science Advisory Board
has since disagreed with the NTP conclusion, interpreting the evidence as `equivocal', and has reaffirmed in its 1985 review a previously reached conclusion, notably that:
the current peer-reviewed evidence for humans and animals does not support the view that asbestos ingested in water causes organ-specific cancers.4 In view of ail these studies, prevailing international scieH| tific opinion is that the public health risk associated with waterborne asbestos is sensibly zero. I Consistent with that opinion is the view of the World Health Organization. WHO drinking water guidelines
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discuss in detail the potential risks of asbestos, but con clude that no guideline value for the substance is necessary.5 In a 1985 letter by its Director of Environmen tal Health Service, WHO reviewed the new data reported since original publication of the guidelines and concluded:
it would, therefore, appear from such scien tific work which has been published since 1981, that the general consensus is that im bibed asbestos via drinking water supplies poses no assessable risk to the health of the consumer.5 Also, the Royal Commission on Matters of Health and Safety Ar ising from the Use of Asbestos in Ontario, Canada published in 1984 an extensive review on all aspects of asbestos risk. The Commission found that some Ontario water supplies contain up to 22 million asbestos fibers per liter but concluded such concentrations are not a public health concern: The fibers are almost invariably extremely short, that is, below one micron in,length. The small dimension of these fibers coupled with our finding that asbestos disease is occa sioned by inhalation rather than ingestion, leads us to conclude that asbestos in drink ing water is not a health hazard.7
V. Asbestos Cement Pipe Asbestos in clay was the first composite building material
used by man, 4000 years ago. Much later, asbestos com bined with cement became the first industrially-recognized fiber-cement material, and was commercially developed into pipe and other products.8
Since its invention at the turn of the century, asbestos cement high- and low- pressure pipes have been used for drinking water distribution, sewage, drainage andeirrigation systems. At least 1.5 million miles of A/C pipe have been installed worldwide. A/C pipe was introduced in the U.S. in 1929, and current estimates of total use in the coun try exceed 400,000 miles,3 in systems that serve at least 26 million people.10
One reason for the presence of asbestos fibers in drink ing water may be related to the method of distribution, i.e. A/C pipe.-fhe issue of fiber release from A/C pipe con tinues to be closely examined by a number of U.S. and in ternational public health organizations. Highly corrosive water, e.g. soft water with a low ph, is much more likely
to attack the cement matrix than are neutral and alkaline waters. Consequently, A/C pipe manufacturers do not recommend their products be used where water is highly aggressive.
It is highly unlikely that fiber release from A/C pipe causes exposure exceeding that which would occur from drinking water from areas geologically-rich in asbestos, i.e. the California Bay and Puget Sound areas.11
Commenting on the issue, a U.S. Environmental Protec tion Agency water quality official in 1983 pointed out, "If
li the source of asbestos in drinking water is [A/C] pipe then
there is more than sufficient economic reason to correct the corrosive action of the water on the pipe."12 In other words, good water treatment by a community is one of the best ways to preserve the integrity of A/C pipe.
More recently, a 1986 World Health Organization memorandum noted, "Generally, it has been concluded that the concentration of asbestos in drinking water resulting from the use of [A/C] pipe does not present a hazard to human health"13
VI. Asbestos Filters Often asbestos has been utilized as a component in
paper filtering materials which are used by food and drug industries. The asbestos fibers are an ideal filtering material because they combine a high surface area with high permeability and enable the efficient clarifying and/or sterilizing of beverages and drugs.
Typical beverages which may be filtered through asbestos include: beer, wine, iiquor and soft drinks.14
Using asbestos to filter liquids has led to the supposi tion that perhaps some fibers can be pleased during the process, and pose a healttyjoncern for consumers. The presence of Asbestos in different beverages has been repeatedly discovered by researchers. However, argument persists over whether the fibers' origin is shedding from filter material or comes from along with the natural water used to make the beverages. Whichever, manufacturers now add, as a standard practice, a non-asbestos trap filter at the end of their process lines.
The 1984, the Report of the Royai Commission on Mat ters ot Health and Safety Arising from the Use of Asbestos ^ in Ontario responded to this issue:
... in view of the fact that asbestos fiber levels I in filtrate do not appear to be significantly
higher than levels in drinking water, we see
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no need for new legislation which would specifically limit the level. . 15
VM. U.S. Government Action --In 1974 and 1975, the Environmental Protection Agen
cy promulgated a set of national waste water effluent stan dards for asbestos manufacturing operations to control the discharge of asbestos-bearing waste to waterways and publicly-owned treatment works.17
--In 1975, the Food and Drug Administration formalized a regulation that restricts the use of asbestos fibers in the manufacture of parenteral drugs for humans. At the same time, FDA reaffirm^! an earlier position, that limits on asbestos filters in preparation of foods and non-parenteral drugs is uncalled for by current, available data.18
--In 1985, the EPA proposed setting a recommended maximum containment level for asbestos in drinking water at 7.1 million long fibers (greater than 10 microns) per liter. The rulemaking is pending.19 If the level becomes a final rule as proposed, almost all, if not all U.S. drinking water will already be in compliance as such concentrations are rarely monitored.
--In 1986, the EPA proposed a ban of asbestos cement pipe, basing its arguments on estimated airborne asbestos fiber exposures in pipe manufacture and installation, not on ingestion risk.20
VIII. Conclusion
Asbestos exists on the earth's surface throughout the
world and is naturally released into water by erosion. For
a very long time this natural level of asbestos has been
making its way into everyone's drinking water. However, the
actual risk associated with the drinking of asbestos in small
amounts has not been identified by public health officials
as significant.
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Asbestos cement pipe is widely recognized as cost-
effective, reliable, and safe as any water pipe in common
use today. In non-aggressive waters, field measurements
have confirmed laboratory results that A/C pipe does not
contribute significant or in many cases even measureable
amounts of asbestos to drinking water carried through it. For aggressive wafers, water stabilization is considered a
positive step towards reducing the possibility of significant
amounts of fiber release.
As of mid-1987, the U.S. Environmental Protection Agency
proposal to ban the use of A/C pipe was still pending.
Strong arguments from industry including several represen tatives of third world countries where the lack of potable water poses serious health problems, had been presented to EPA against the ban and the Agency was still recon sidering the matter.
IX. References
1. J.R. Millette, et at., "Asbestos in Water Supplies in the
.. United States," 53 Environ. Health Perspect. 45 (Nov.
1983).
2. B.T. Commins, "Asbestos Fibres in Drinking Water",
Scientific and Technical Report (May 1983).
3. ibid, at 43.
4. Letter from the SAB to EPA Administrator Lee M.
Thomas (July 30, 1985).
5. WHO, Guidelines For Drinking-Water Quality Vol. 1 at
53, Vol. II at 68-75 (1984).
6. Letter from J.l. Waddington, Director, Environmental
Health Service, World Health Organization to Sir
Neville Stack, Director General, Asbestos International
Association (Nov. 29, 1985).
7. Report of the Royal Commission on Matters of Health
and Safety Arising from the Use of Asbestos in Ontario,
Ontario Ministry of Labor (1984), at 15.
8. Asbestos/Cement Pipe Corrosion Part l-Historical,
Technological, Economic and Statistical Background,
Energy Mines and Resources Canada (Oct. 1983), at 1.
9. Commins, at 17.
10. Draft Final Report Exposure Assessment For Asbestos, U.S. Environmental Protection Agency (Jan. 9, 1984),
at 246.
11. Ibid.
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12. J. Cotruvo, Office of Drinking Water, U.S. Environmen
tal Protection Agency, 53 Environmental Health
Perspectives 181 (Nov. 1983).
13. WHO.
14. Chemical Market Input/Output Analysis of Selected
Chemical Substances to Assess Sources of
vironmental Contamination, Task Ill-Asbestos, U.S. En
vironmental Protection Agency (Aug. 1978), at 177.
i 15. Ontario Royal Commission, at 654-57.
16. Chemical Market Input/Output Analysis, at 180.
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17. 40 CFR Part 427. 18. 21 CFR Part 133. 19. Notice of Proposed Rulemaking for National Primary
Drinking Water Regulations, U.S. Environmental Pro tection Agency, 50 Fed. Reg. 46,936 (Nov. 13, 1985). 20. Notice of Proposed Rulemaking under Toxic Substances Control Act on Asbestos: Proposed Min ing and Import Restrictions and Proposed Manufac turing, Importation, and Processing Prohibitions, U.S. Environmental Protection Agency, 51 Fed. Reg. 3737 (Jan. 29, 1986).
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