The following resolution is being submitted to the American Public
Health Association by Myron Coplan, chemical engineer, & Dr. Robert
Carton, past-President of EPA Headquarters Union for consideration
at APHA's October 21-25, 2001, conference in Atlanta, Georgia.
Silicofluorides Should
Not Be Added to Municipal Water Without Safety Testing Adequate
to Protect Children and Other Vulnerable Populations
The American Public Health Association,
Recognizing that the APHA has had a consistent and long-standing
policy of endorsing water fluoridation as a public health measure
in Policy Statements 5005, 5508, 5607, 5904, 6912, 8402, and 7911,
and
Recognizing also that said endorsement has traditionally been predicated
on the belief that fluoride is a valuable caries preventive whose
benefits can be enjoyed without adverse health effects by regular
ingestion of water treated to an appropriate level of fluoride ion
derived from an appropriate source, and
Recognizing that none of the recited APHA Policy Statements took
into account the fact that there had been no health safety testing
of specific water fluoridating agents known as the silicofluorides
(H2SiF6 and Na2SiF6, henceforth
SiFs) when their use began; and
Recognizing that water systems providing 91 percent of U.S. fluoridated
water, and serving 140 million people, 1 dispense 200,000
tons per year of SiFs 2 and these agents have been used
since 1947 3 without tests of their health safety 4,
5 and
Recognizing that a 1952 request by a Select Congressional Committee
(82nd Cong., 2d Session) for studies to determine
the long-range effects upon the aged and chronically ill of the
ingestion of water containing inorganic fluorides 6
has yet to be addressed regarding health safety of the silicofluorides
while animal health studies of fluoridated water, including those
conducted by the National Institute of Health's National Toxicology
Program, regularly employ sodium fluoride (NaF), the first fluoridating
compound used (in 1945), and not SiFs, the principal agents currently
added to water; 7,8,9,10,11,12,13,14,15,16 ; and
Further recognizing that, claims to the contrary,17 SiF
treated water is not like NaF treated water because [SiF6]
2- (a) is unlikely to dissociate completely under water
plant conditions, producing only free fluoride and silicic acid
without side reactions;18, 19 (b) is likely to react
with Al(OH)3 to produce several derivative compounds;
(c) dissociation status depends on pH and concentration so that
incompletely dissociated SiF residues may re-associate both at intra-gastric
pH around 2.0 20 and during food preparation, producing
SiF species including silicon tetrafluoride, (SiF4),
a known toxin; 21, 22, 23, 24, 25, 26 and (d) commercial
SiFs are likely to be contaminated with fluosiloxanes, 27 arsenic
and heavy metals, 28 and radionuclides,29
since they are waste products from fertilizer manufacture and uranium
extraction from phosphate rock 30, 31, 32, 33
Recognizing that in 1950,34 the U.S. Public Health Service
endorsed Na2SiF6 as a cheaper alternative
for NaF, reasoning that equal fluoride uptake by hard tissues demonstrated
the biological equivalence of NaF and Na2SiF6,
although earlier animal studies 35 had shown that when
equal amounts of fluoride were ingested and the total amount of
fluoride excreted was also equal, animals exposed to NaF eliminated
more fluoride in feces, while animals exposed to Na2SiF6
eliminated three-fold more fluoride in urine, thus indicating circulating
blood fluoride levels; and
Recognizing that a 1975 German study found that acetylcholinesterase
inhibition, (the intended action of the high-risk organophosphate
and carbamate pesticides widely used in agriculture and around residences),
is many-fold more severe due to the SiF complex (and other complexes
such as with iron) as compared to the simple fluoride ion released
by NaF, which is itself an acetylcholinesterase inhibitor;36
and
Noting that dental fluorosis (pre-eruption F-induced tooth enamel
malformation) expected in 1945 to be only mild and prevail at 10-12
percent in optimally fluoridated areas,37
now averages over 25 percent, and sometimes exceeds 80 percent in
said optimally fluoridated areas with many moderate
to severe cases;38 and
Further noting that a 1983 expert panel appointed by the Surgeon
General to review non-dental health effects of ingested
fluoride was instructed to limit its scope to death (poisoning),
gastrointestinal hemorrhage, gastrointestinal irritation, arthralgias,
and crippling fluorosis thus essentially ignoring many possible
effects in children; 39 and
Considering that data on 400,000 children in New York, Massachusetts,
and in the NHANES III (National Health and Nutrition Examination
Survey III) study, found that where local water is fluoridated with
SiFs the prevalence of children with venous blood lead exceeding
10mcg/dL was significantly higher than in non-fluoridated areas
with risk ratios of between 2.0 and 4.0 (p<0.001) controlling
for race, housing age, poverty, congestion, and parental education);40,
41and
Recognizing that blood lead is believed responsible for adverse
effects inflicted in utero such as impaired immune capacity,42
brain damage and developmental problems,43, 44,
45 as well as in early childhood,46, 47, 48,
49, 50, 51and into puberty/adolescence
as impaired cognition and impulse control,52, 53and adulthood
as nephropathy and hypertension,54, 55and
into geriatric life;56 and
Finally, recognizing that dental caries prevalence rates in optimally
fluoridated areas today is indistinguishable from prevalence
rates in non-fluoridated areas 57, 58, 59,
60, 61, 62, 63; and
Noting that the Journal of the American Dental Association has
recently published a comprehensive study showing that ingestion
of fluoride does not benefit teeth in their pre-eruptive stage,
but only via by topical contact after tooth eruption;64 and
Noting also that seven times in the past APHA has in one way or
another endorsed fluoridation of public water supplies but none
of the relevant POLICY STATEMENTS explicitly endorsed any specific
fluoridating agent, whereas POLICY STATEMENT 6912 implicitly did
so by identifying fluoridation in Grand Rapids in 1945 which, according
to Reference 3, was initially accomplished by adding sodium fluoride
to its water supply; and
Noting, moreover, that less than 10% of US fluoridated water today
is treated with sodium fluoride while over 90% is treated with one
of the SiFs which have never been tested for health safety; and
Further noting that the premise that fluoride is fluoride
whatever its source is false and dangerously misleading based on
evidence that water treated with SiFs is not just like water treated
with sodium fluoride as confirmed by (a) epidemiological analyses
of several health and behavioral effects comparing communities using
SiFs with communities using sodium fluoride or not adding fluoride;
(b) biological studies comparing effects of ingested water treated
with sodium fluoride with effects of ingested water treated with
SiFs; (c) disputed assurances concerning the virtually total
dissociation of the SiFs under real use conditions; (d) an advisory
letter from the Director of the EPA Water Supply and Water Resources
Division in a letter67 dated March 15, 2001 summarizing
the position of the highest scientific authorities of the EPA reached
in January 2001 which notes the following:
Several fluoride chemistry related research
needs were identified including; (1) accurate and precise values
for the stability constants of mixed fluorohydroxo complexes [read
silicofluoride dissociation residues] with aluminum
(III), iron (III) and other metal cations likely to be found under
drinking water conditions and (2) a kinetic model for the dissociation
and hydrolysis of fluosilicates and stepwise equilibrium constants
for the partial hydrolysis products.
thus admitting that EPA scientific leaders are not
satisfied with assurances given by their own technical staffs of
the health safety of SiFs on two counts: (i) possible formation
of toxic complexes with aluminum, iron and other cations commonly
present in water plant water and (ii) potential toxic effects from
SiF dissociation residues in municipal drinking water that may be
present despite predictions made by EPA and others for SiF dissociation.
Citing APHA's explicit endorsement of the precautionary principle
as a cornerstone of preventive public health policy, especially
in order to protect the health and well-being of all developing
children;65 and Presidential Executive Order #13045
calling on all federal agencies to ensure that all federal environmental
health policies and regulations consider the special sensitivities
and vulnerabilities of children;66
The APHA, therefore:
- Calls for the establishment of an APHA study committee comprising
an equal number of members from the Environment and Oral Health
Sections plus a representative of the APHA Directorship to investigate
in depth water fluoridation using silicofluorides on the basis
that they have never been tested for health safety in humans and
may be particularly hazardous to children, the aged and the chronically
ill;
- Calls for the National Institute of Environmental Health Science/National
Toxicology Program to nominate the silicofluorides for priority
CCL status to undertake a full battery of chronic health effects
testing of silicofluoride treated water; and
- Calls for the US. EPA to review its standards for the safe level
of fluoride exposure in the light of any NTP results arising under
actions requested above.
-------------------------------------
Myron J. Coplan, P.E.* (APHA
#9774108)
Intellequity Technology Services
Natick, MA 01760
(ph) 508-653-6147 (fax) 508-655-3677
Robert J. Carton, Ph.D.** (APHA #9774839)
Environmental Coordinator
U.S. Army Medical Research & Materiel Command
Fort Detrick, MD 21702-5012
(ph) 310-610-2004 (fax) 1-301-619-7803
Robert.Carton@det.amedd.army.mil
* Contact author
**The views presented in this resolution are those of its authors
(MJC and RJC) and do not necessarily represent the views of the
Department of Defense.
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