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An Appeal to the Scientific, Academic and
Professional Communities World-Wide, Requesting Scientific Integrity
in Addressing the Issue of Water Fluoridation
The following attendees of the XXVth conference of the International
Society for Fluoride Research held in Dunedin, New Zealand
in January of 2003, resolved to call upon our colleagues in the
scientific, academic and professional communities, and all others
actively promoting sound public health policies worldwide, to help
bring scientific integrity to the issue of water fluoridation. (Please
note that the ISFR organization itself does not take a position
on the fluoridation debate.)
Our primary focus with this initiative is to encourage more scientists,
academics and professionals to examine this controversial issue
with an open mind and ensure that it is resolved scientifically
and ethically. From the viewpoint of good scientific method and
scholarship, it is unacceptable that spokespersons for several governments
practicing fluoridation repeatedly claim that the practice is 'safe
and effective', while refusing to subject the issue to open public
debate. This refusal allows them to wrongly claim that the arguments
mobilized by opponents of fluoridation are ‘junk science’
when in fact most of the opponents’ evidence is based upon
peer-reviewed literature, including important articles written by
advocates of fluoridation themselves.
The signatories to this Appeal take the position that biased
reviews; misrepresentation and censorship of results; a failure
to collect the basic data; intimidation and harassment of opponents,
as has happened in the case of Dr William Marcus, Dr John Colquhoun,
Dr Bruce Spittle, Dr Phyllis Mullenix, Dr Mark Diesendorf and Dr
Hardy Limeback, to name a few, have no place in science. In this
appeal we first list 13 principal scientific findings that concern
us. Then we present the petition, which spells out the steps we
believe have to be taken to ensure that this issue is resolved properly.
These findings are:
1. Topical not systemic mechanism
The mechanisms of action of fluoride in reducing tooth decay are
now widely accepted to be predominantly topical,
i.e. acting directly on the surface of teeth, not systemic (CDC,
1999, 2001). In other words, there is no credible justification
for requiring people to swallow fluoride.
2. No deficiency
No-one has ever been identified as having a genuine deficiency
of fluoride. Fluoride, in the mg/day doses recommended by proponents
of fluoridation, is not an essential nutrient.
3. Negligible benefits
A major cross-sectional survey of 84 cities in the USA by the National
Institute of Dental Research found that children (aged 5 to 17)
who had lived their whole lives in fluoridated cities had on average
only 0.6 fewer decayed, missing and filled tooth surfaces (DMFS)
per child than those in unfluoridated cities (Brunelle & Carlos,
1990). In Australia a survey by pro-fluoridationists found an average
reduction of only 0.12 to 0.3 DMFS per child (Spencer, Slade &
Davies, 1996). Since the total number of permanent tooth surfaces
in a child's mouth is 128, the US and Australian reductions are
less than one half and one quarter of one percent of tooth surfaces,
respectively. Both are negligible.
4. Excellent teeth in unfluoridated areas
Since the 1960s tooth decay has declined dramatically in both fluoridated
and non-fluoridated regions of the vast majority of developed countries.
Indeed, WHO figures, available online,
show that in non-fluoridated countries, including most of Europe,
tooth decay in 12 year-olds is just as good, if not better than
in fluoridated ones. In several cases this decline also commenced
in fluoridated places before fluoridation and the uses of any other
fluorides were implemented. Clearly, factors other than fluoridation
and fluorides must be playing a major role (Diesendorf, 1986; Colquhoun,
1988; De Liefde, 1998). In five recent studies it has been shown
that when fluoridation was discontinued in communities in Finland,
Cuba, former East Germany and British Columbia, tooth decay did
not go up, but continued to go down (Maupome et al, 2001; Kunzel
and Fischer,1997, 2000; Kunzel et al, 2000, and Seppa et al, 2000).
5. Medication with uncontrolled dose
Fluoridation is medication with uncontrolled dose (Diesendorf,
1995). The daily fluoride dose received by people ingesting drinking
water fluoridated at a concentration of 1 ppm varies widely with
water intake (Ershow & Cantor, 1989), diet, and kidney function.
Those with high fluoride intake include athletes, outdoor laborers,
people with diabetes, people with kidney damage and bottle-fed infants.
6. High dose to bottle-fed infants
In particular, bottle-fed infants, who ingest milk formula reconstituted
with fluoridated water, receive a daily fluoride dose that is 100
times that of breast-fed infants and at least 4-6 times that recommended
by medical authorities for fluoride supplementation in unfluoridated
areas (Diesendorf & Diesendorf, 1997).
7. Dental fluorosis is rampant
When fluoridation was originally proposed, proponents claimed that
it would only cause ‘mild’ or even milder types of dental
fluorosis (fluoride-induced mottling of teeth) in 10% of the community
and no ‘moderate’ or ‘severe’ types. However,
in practice, because of the combined exposure to both fluoridated
water and other sources, the prevalence and severity of dental fluorosis
has increased far beyond initial expectations. The York Review (McDonagh
et al, 2000) estimates that up to 48% of children in fluoridated
areas have some form of dental fluorosis. Even children in unfluoridated
areas have dental fluorosis rates exceeding those thought to be
associated with the ‘optimal dose’ originally proposed
to prevent dental decay (Heller, et al. (1997).
8. Skeletal fluorosis and arthritis
Over a lifetime fluoride accumulates in bones, adding mass but
gradually destroying bone structure. The disease of bones and joints,
skeletal fluorosis, has been reported in the medical literature
to be observed in naturally fluoridated areas of several countries
where fluoride concentrations in drinking water are less than 4
ppm and in several cases where they are less than or equal to 1
ppm (Singh et al, 1961; Singh et al, 1963; Siddiqui, 1970; Jolly
et al, 1973). Of particular concern is the fact that the early symptoms
of skeletal fluorosis are identical to arthritis, and the incidence
of arthritis is increasing rapidly in several fluoridated countries.
In America, one in three Americans have arthritis (CDC, 2002). Incredibly,
there has been no attempt to check the fluoride levels in the bones
of those inflicted by this disease. There have been no scientifically
adequate studies of the prevalence of skeletal fluorosis in developed
countries.
9. Hip and other bone fractures are a hazard
Many people in fluoridated communities will receive a cumulative
dose of fluoride during their lifetimes that exceeds the cumulative
dose which in clinical trials of large daily fluoride doses over
a short period of time clearly increases hip fracture rates (Riggs
et al, 1990). Furthermore, in the majority of epidemiological studies
conducted since 1990, a higher rate of hip fractures has been found
in artificially fluoridated areas compared with unfluoridated areas
(www.SLweb.org/fluoride-bone.html).
In particular, a recent epidemiological study, which examined the
elderly in six naturally fluoridated Chinese villages, hip fracture
rates doubled at 1.5 ppm, and tripled at 4.3 ppm, when compared
to the fracture rates at 1 ppm fluoride (Li et al., 2001). This
finding again suggests a very small (if any) safety margin for such
a serious outcome. In Mexico, Alarcon-Herrera et al (2001) have
shown a linear correlation between the severity of dental fluorosis
and the incidence of bone fractures in children.
10. Inadequate safety factor
In order to protect members of the population at greatest risk,
toxicology generally requires a safety factor of 100 between ingested
and unsafe concentrations of environmental chemicals. This allows
for variations in individual exposures and individual sensitivities,
which each receive a factor of 10. However, in the USA the maximum
contaminant (i.e. unsafe) level for fluoride in drinking water was
unscientifically set at 4 ppm providing a safety factor of only
4 for water fluoridated at 1 ppm. This is based on the fluoride
concentration at which it is officially accepted that some people
will suffer from skeletal fluorosis in the USA, despite the fact
that in some other countries this disease is occasionally seen at
1 ppm or less. Based on evidence mentioned in this Appeal, the safety
factor for hip fractures is a factor or 4 (or possibly as low as
1.5, see Li et al, 2001); less than 3 for lowered fertility (Freni,
1994), possibly 1 for the uptake of aluminum into the brain (Varner
et al, 1998) and definitely 1 for dental fluorosis. In practice,
even with a safety factor of 4, some people with high
intakes of water fluoridated at 1 ppm could consume the same daily
fluoride dose as people with average intakes
of water containing 4 ppm fluoride. So, in reality, in terms of
the fluoride doses that they ingest, there is no safety margin for
these people for any of the above diseases.
11. Hypersensitivity/intolerance reactions
There is large body of clinical reports that some people suffer
from hypersensitivity or intolerance reactions to fluoride in drinking
water, tablets and toothpaste. These symptoms (which include excessive
fatigue, excessive thirst, gastric distress, muscular weakness,
etc) are reversed when the source of fluoride is removed and have
been observed under double blind conditions (Waldbott, Burgstahler
& McKinney, 1978; Grimbergen, 1974). Inexplicably, these studies
have been dismissed out of hand by government agencies which have
never followed them up in any systematic fashion.
12. Numerous biological effects
Laboratory and animal experiments show that fluoride is highly
active biologically. Emsley et al (1981) have shown that fluoride
forms a strong hydrogen bond with the groups found in proteins and
nucleic acids. In vitro experiments demonstrate that fluoride inhibits
enzymes; induces chromosome aberrations (Susuki and Tsutsui, 1989);
genetic mutations (Caspary et al, 1987) and in the presence of aluminum
disrupts G-proteins (Strunecka and Patocka, 2002). Animal experiments
reveal that fluoride increases the uptake of aluminum into the brain
at 1 ppm in the drinking water (Varner et al, 1998). At higher doses
fluoride causes reproductive problems (Chinoy and Narayana,1994)
and could be a weak promoter (Taylor and Taylor, 1965) and inducer
of cancer (NTP, 1990). In US counties with 3 ppm fluoride in the
water there is a significant decrease in human fertility (Freni,
1994). Also, in humans, fluoride accumulates in the pineal gland
(Luke, 2001) and in animals it lowers melatonin production (Luke,
1997).
13. Industrial waste as a medication
The agents which are used to fluoridate over 90% of the water treated
in the US (hexafluorosilicic acid and its sodium salt) are waste
materials obtained from the pollution scrubbers of the phosphate
fertilizer industry and contain trace amounts of arsenic, lead and
other toxic chemicals. Even in their pure state the US EPA confirms
that the silicofluorides have never been subjected to chronic testing
in animals. However, in two epidemiological studies they have been
shown to be associated with a greater uptake of lead into children's
blood and increased violent behavior (Masters & Coplan, 1999,
2000).
On the following page is the petition
we hope that you will wish to sign.
SIGNED:
Dr. Miklos Bely,
National Institute of Rheumatology,
Budapest, Hungary.
Dr. Albert Burgstahler,
Professor Emeritus in Organic Chemistry,
University of Kansas,
Lawrence, Kansas, USA.
Dr. N. J.Chinoy,
Zoology Department,
Gujarat University,
Ahmedabad, Gujarat, India.
Dr. Paul Connett,
Professor of Chemistry,
St. Lawrence University,
Canton, NY, USA.
Dr. Mark Diesendorf,
Director, Sustainability Centre Pty Ltd,
Sydney, Australia.
Dr.William J. Hirzy,
Vice-President,
National Treasury Employees Union, Chapter 280,
US EPA, Washington, DC, USA.
Dr. Hardy Limeback,
Head of Preventive Dentistry,
University of Toronto,
Toronto, Canada.
Dr. Bruce Spittle,
Senior Lecturer,
Department of Psychological Medicine,
University of Otago,
Dunedin, New Zealand.
Dr. Anna Strunecka,
Professor of Physiology,
King Charles University,
Prague, Czech Republic.
* * *
We cannot hope in the space available to present all our concerns
(that would take a book) or both sides of the issue. Hopefully we
have said enough to spark your interest and you will find out more
for yourselves. The pro-fluoridation position is articulated at
the American Dental Association web page www.ada.org;
the anti-position is further elaborated at www.fluoridealert.org
and a comprehensive and annotated bibliography can be found a www.SLweb.org/bibliography.html,
where all the references noted above can be found.
THE PETITION
A Petition to all Governments Practicing, and all Organizations
Supporting, Water Fluoridation
We, the undersigned members of the scientific, academic and professional
communities, and others promoting sound public health policy worldwide,
call upon professional associations and government agencies in Australia,
Brazil, Canada, Ireland, Israel, Malaysia, New Zealand, Singapore,
South Africa, the UK and the US, to bring scientific integrity to
the issue of water fluoridation. To this end, we urge them:
1) To examine carefully all the literature
which pertains to fluoridation's dangers and benefits, in an open,
honest and transparent manner. We urge them to hear from experts
on both sides of this issue who are prepared to give their testimony
under oath before a truly independent scientific panel, the membership
of which is approved by both sides.
2) To collect fundamental data such as fluoride levels in the bones
and pineal glands, measured during autopsy, and the prevalence of
skeletal fluorosis and hypersensitivity/intolerance to fluoride,
of those who have lived for various lengths of times in fluoridated
areas, as well as using dental fluorosis (tooth mottling) as a bio-marker
to investigate the possible dangers to children of being exposed
to excessive levels of fluoride at an early age.
3) To halt immediately the practice of using untested and industrial
grade waste materials (such as hexafluorosilicic acid from the phosphate
fertilizer industry) in water fluoridation programs.
4) To renounce the use of any intimidatory pressures on those professionals
whose research or review has led them to adopt an anti-fluoridation
position.
5) To renounce the widespread practice of misrepresenting scientific
results in order to achieve the fluoridation of more water supplies.
6) Either to defend water fluoridation in open public debate or
to halt the practice forthwith.
Click here to see the list of Signatories
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