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new class of water pollutants has been
discovered during the past six years.[1] Pharmaceutical drugs given to people
and to domestic animals including antibiotics, hormones, strong pain killers,
tranquilizers, and chemotherapy chemicals given to cancer patients are being
measured in surface water, in groundwater and in drinking water at the tap.
Large quantities of drugs are excreted by humans and domestic animals, and
are distributed into the environment by flushing toilets and by spreading
manure and sewage sludge onto and into soil.
German scientists report that anywhere
from 30 to 60 drugs can be measured in a typical water sample, if anyone
takes the time to do the proper analyses.[2] The concentrations of some
drugs in water are comparable to the low parts-per-billion (ppb) levels
at which pesticides are typically found.[1] To some people this is reassuring,
but others are asking, "What is the long-term effect of drinking, day
after day, a dilute cocktail of pesticides, antibiotics, pain killers, tranquilizers
and chemotherapy agents?" Of course no one knows the answer to such
a question it is simply beyond the capabilities of science to sort out the
many chemical interactions that could occur in such a complex chemical soup.
The only solution to such a problem would be prevention.
The first study that detected drugs
in sewage took place at the Big Blue River sewage treatment plant in Kansas
City in 1976. The problem was duly recorded in scientific literature and
then ignored for 15 years.[3] In 1992, researchers in Germany were looking
for herbicides in water when they kept noticing a chemical they couldn't
identify.[4] It turned out to be clofibric acid (CA), a drug used by many
people in large quantities (1 to 2 grams per day) to reduce cholesterol
levels in the blood.[1] Clofibric acid is 2-(4)-chlorophenoxy-2-methyl propionic
acid, a close chemical cousin of the popular weed killer 2,4-D.1 Based on
that early discovery, the search for clofibric acid (CA) in the environment
was stepped up.
Since 1992, researchers in Germany,
Denmark and Sweden have been measuring CA and other drugs in rivers, lakes,
and the North Sea. To everyone's surprise, it turns out that the entire
North Sea contains measurable quantities of clofibric acid. Based on the
volume of the Sea, which is 12.7 quadrillion gallons (1.27 x1016 gallons),
and the average concentration of CA, which is 1 to 2 parts per trillion
(ppt), researchers estimate that the Sea contains 48 to 96 tons of clofibric
acid with 50 to 100 tons entering the Sea anew each year.[1] The Danube
River in Germany and the Po River in Italy also contain measurable quantities
of clofibric acid.[5,6] Of more immediate concern to humans is the finding
that tap water in all parts of the city of Berlin contains clofibric acid
at concentrations between 10 and 165 ppt.[5] The water supplies of other
major cities remain to be tested.
As a result of this European work,
a few U.S. researchers are now beginning to pay attention to drugs in the
environment. Individual scientists within the U.S. Food and Drug Administration
(FDA) have been concerned about this problem for a decade,[7] but so far
FDA has taken the official position that excreted drugs are not a problem
because the concentrations found in the environment are usually below one
part per billion (ppb).[2]
Drugs are designed to have particular
characteristics. For example, 30 percent of the drugs manufactured between
1992 and 1995 are lipophilic, meaning that they tend to dissolve in fat
but not in water.[8] This gives them the ability to pass through cell membranes
and act inside cells. Unfortunately, it also means that, once they are excreted
into the environment, they enter food chains and concentrate as they move
upward into larger predators. Many drugs are also designed to be persistent,
so that they can retain their chemical structure long enough to do their
therapeutic work. Unfortunately, after they are excreted, such drugs also
tend to persist in the environment. A landfill used by the Jackson Naval
Air Station in Florida contaminated groundwater with a plume of chemicals
that has been moving slowly underground for more than 20 years. The drugs
pentobarbital (a barbiturate), meprobamate (a tranquilizer sold as Equanil
and Miltown) and phensuximide (an anticonvulsant) are still measurable in
that groundwater plume.[8]
When a human or an animal is given a
drug, anywhere from 50 percent to 90 percent of it is excreted unchanged.
The remainder is excreted in the form of metabolites chemicals produced
as byproducts of the body's interaction with the drug. Researchers report
that some of the metabolites are more lipophilic and more persistent than
the original drugs from which they were derived. Because of the complexity
of the chemistry involved in drug metabolism, and the interactions of the
metabolites with the natural environment, Danish researchers say is it "practically
impossible to estimate predicted environmental concentrations (PEC) of any
medical substances with available knowledge."[8]
Yet U.S. regulatory policy for new drugs
depends entirely upon estimating concentrations that might result from excretion.
When a new drug is proposed for market, FDA requires the manufacturer to
conduct a risk assessment that estimates the concentrations that will be
found in the environment. If the risk assessment concludes that the concentration
will be less than one part per billion, the drug is assumed to pose acceptable
risks.[2] FDA has never turned down a proposed new drug based on estimated
environmental concentrations, and no actual testing is conducted after a
drug is marketed to see if the environmental concentration was estimated
correctly.
German chemists have found that many
drugs can be measured at environmental concentrations that exceed one ppb.
And of course several drugs measured together can exceed one ppb. Furthermore,
there is ample evidence from research conducted during the past decade showing
that some chemicals have potent effects on wildlife at concentrations far
below one ppb. For example estradiol, the female sex hormone (and a common
water pollutant), can alter the sex characteristics of certain fish at concentrations
of 20 ppt, which is 1/50 of one ppb.[2]
Another problem resulting from drugs
in the environment is bacteria developing resistance to antibiotics. The
general problem of antibiotic-resistant bacteria has been recognized for
more than a decade. Antibiotics are only useful to humans so long as bacteria
do not become resistant to their effects. Hospital sewage systems discharge
substantial quantities of antibiotics into the environment.[9] Bacteria
exposed to antibiotics in sewage sludge or water have an opportunity to
develop resistance. Janet Raloff of Science News quotes Stuart Levy, who
directs the Center for Adaptation Genetics and Drug Resistance at Tufts
University in Boston, saying, "[T]hese antibiotics may be present at
levels of consequence to bacteria levels that could not only alter the ecology
of the environment but also give rise to antibiotic resistance."[2]
What can we learn from the emergence
of this new problem?
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References
1. Hans-Rudolf Buser and Markus D. Muller, "Occurrence
of the Pharmaceutical Drug Clofibric Acid and the Herbicide Mecoprop in
Various Swiss Lakes and in the North Sea," Environmental Science And
Technology Vol. 32, No. 1 (1998), pgs. 188-192.
2. Janet Raloff, "Drugged Waters," Science News
Vol. 153, No. 12 (March 21, 1998), pgs. 187-189.
3. C. Hignite and D.L. Azarnoff, "Drugs and drug metabolites
as environmental contaminants: chlorophenoxyisobutyrate and salicyclic acid
in sewage water effluent," Life Sciences Vol. 20, No. 2 (January 15,
1977), pgs. 337-341.
4. H.J. Stan and Thomas Heberer, "Pharmaceuticals
in the Aquatic Environment," Analusis Magazine Vol. 25, No. 7 (1997),
pgs. M20-M23.
5. Thomas Heberer and H.-J. Stan, "Determination of
Clofibric Acid and N-(phenylsulfonyl)-Sarcosine in Sewage, River, and Drinking
Water," International Journal Of Environmental Analytical Chemistry
Vol. 67 (1997), pgs. 113-124. And see: Thomas Heberer and others, "Detection
of Drugs and Drug Metabolites in Ground Water Samples of a Drinking Water
Treatment Plant," Fresenius Environmental Bulletin Vol. 6 (1997), pgs.
438-443.
6. "Pille im Brunnen [Pills in the Fountain],"
Der Spiegel No. 26 (June 24, 1996), pgs. 154-155, translated for us by Thea
Lindauer, Annapolis, Maryland.
7. Personal communication from Maurice Zeeman, U.S. Environmental
Protection Agency, March, 1998.
8. B. Halling-Sorensen and others, "Occurrence, Fate
and Effects of Pharmaceutical Substances in the Environment A Review,"
Chemosphere Vol. 36, No. 2 (1998), pgs. 357-393.
9. Andreas Hartmann and others, "Identification of
Fluoroquinone Antibiotics as the Main Source of umuC Genotoxicity in Native
Hospital Wastewater," Environmental Toxicology And Chemistry Vol. 17,
No. 3 (1998), pgs. 377-382.
10. T. Steger-Hartmann and others, "Biological Degradation
of Cyclophosphamide and Its Occurrence in Sewage Water," Ecotoxicology
And Environmental Safety Vol. 36 (1997), pgs. 174-179.
11. Contact: Charlotte Brody, Health Care Without Harm,
c/o CCHW Center for Health, Environment and Justice, P.O. Box 6806, Falls
Church, Virginia 22040. Phone (703) 237-2249. See www.noharm.org. |