Public perceptions and scientific evidence for perceived harms/risks of community water fluoridation: an examination of online comments pertaining to fluoridation cessation in Calgary in 2011.
Podgorny, Paulina C. ; McLaren, Lindsay
Community water fluoridation refers to the controlled addition of
industrial-grade fluoride compounds to public water supplies with the
goal of preventing dental decay. (1) In Canada, the optimal fluoride
concentration to promote dental health is 0.7 mg/L, with a maximum
acceptable concentration (MAC) of 1.5 mg/L. (2) The evidence base for a
beneficial effect of fluoride on tooth decay is substantial. In addition
to its antibacterial activity against cariogenic bacteria, fluoride
exerts a positive effect on tooth remineralization through its
absorption into the surface of enamel crystals as it flows over the
teeth, protecting against dissolution by bacterial acids. (3) Research
also supports the benefits of fluoridated water for preventing tooth
decay, in Canada (4,5) and and elsewhere. However, a systematic review
of research on water fluoridation and health concluded that overall the
evidence base is of low to moderate quality. (6)
Opposition to fluoridation has existed as long as the intervention
itself, and the main reasons have not changed: skepticism about its
effectiveness, concern about its potential harms and resistance to its
intrusive nature. Recently, opposition has materialized in decisions by
several communities in Canada to discontinue the practice. (7,8) While
the proportion of Canadians exposed to community water fluoridation
increased from 6% (1960) to 45% (2007), there has been a decline since
2007 because several large municipalities have discontinued the
practice, including Calgary (2011), Waterloo (2010), Windsor (2013),
Quebec City (2008) and Moncton (2012).
In terms of the risks/harms associated with fluoridation, research
has consistently shown an association between fluoride exposure and risk
of dental fluorosis (staining of the tooth enamel). (9) There is less
support for other harms. The MAC of 1.5 mg/L set out by Health Canada
was identified on the basis that it is "unlikely to cause adverse
health effects", including immunotoxicity, developmental toxicity
and/or neurotoxicity. (2) A recent report by Public Health England (PHE)
confirmed the absence of association between fluoridation status and a
range of adverse health outcomes. (10)
Despite these (and other) reports, there remains concern about
various harms/risks of fluoridation among some members of the public.
(11) Understanding these concerns is important from the point of view of
public health communication. For example, if communication is premised
on disseminating information from scientific studies, it may be less
effective for those who are more influenced by other factors. Sandman
describes this phenomenon in his discussion of hazard and outrage in the
public perception of risk. Whereas experts may understand risk in terms
of magnitude and the probability of an unfavourable event
("hazard"), the public may see risk as a combination of hazard
and outrage factors (e.g., fear, dread, misery). (12)
In Calgary, fluoridation was discontinued in May 2011, following a
City Council vote. Comments on online forums (i.e., online discussion
sites where individuals can hold conversations in the form of posted
messages) provide an opportunity to investigate what the public
perceives to be the harms/risks of fluoridation. Decisions about
fluoridation are made at the municipal level in Canada, within
provincial guidelines (if any). Although a systematic study of
fluoridation decision-making in Calgary in 2011 has not been undertaken,
anecdotal reports suggest that important factors included the need for
an infrastructure upgrade (and associated cost), efforts by a veteran
councillor to revisit fluoridation, and a City Council characterized by
several new councillors and a new mayor. (13-15) Unlike previous
instances of fluoridation decision-making in Calgary (i.e., in 1989 and
1998), when a public vote (plebiscite) was undertaken, the 2011 decision
was made by City Council. The decision-making process happened quickly,
with limited public engagement and essentially none prior to January
2011. (13,14)
The study objective was to identify the health risks, perceived by
some members of the public, associated with water fluoridation as
expressed in online forums relating to its cessation and aftermath in
Calgary (January 2011-) and to systematically examine their scientific
basis. Research questions were as follows: 1) which harms/risks are
mentioned, 2) for those harms/risks, what kinds of evidence are cited,
3) to what extent is scientific literature cited, and what is its
quality, and 4) for a subset of risks/harms, what is known from the
broader scientific literature?
METHODS
Identification of online comments about perceived harms/risks of
fluoridation
A professional health sciences librarian was consulted to establish
an optimal (sensitive and specific) search strategy. Three known links
relating to fluoridation in Calgary were used to validate the search
strategy; that is, we ensured that the search captured links known to be
relevant. (7) The search was conducted in May 2014 and considered
materials from January 2011 (as noted above, little if any discussion
occurred before then) to May 2014.
First, a series of free-text searches, using Google[TM], was
conducted using 1) "fluorid Calgary" (~373,000 results), 2)
"fluoride Calgary" (~182,000 results), 3) "fluoridation
Calgary" (~24,600 results) and 4) "water fluoridation
Calgary" (~12,300 results). Results were listed in order of
relevance (i.e., default setting), with no additional filters. Beginning
with the top result of each search, each webpage was opened to assess
its content. Those webpages that allowed for public comments were
included as a potential source. Webpages that did not allow for
comments, or had zero comments, were excluded. In viewing multiple pages
of results for each search, we observed that the relevance of comments
to our study (fluoridation in Calgary) dropped after the 8th or 9th
page. We therefore decided to examine all results within the first 10
pages for each search. Many items from the first search (i.e., using the
search terms "fluorid Calgary") appeared again in subsequent
searches. Duplicate items were omitted.
Next, for each webpage from the original searches, we pursued
"related articles", "related links" and any
additional webpages cited in the text. Related links that allowed for
comments and had at least one comment were added as sources. Most
"related links" had either already been identified in the
original search, did not have the capacity for comments, had zero
comments or were unrelated to water fluoridation. Finally, search
engines available on the webpages of the Calgary Herald, the Calgary
Sun, The Globe and Mail, the National Post, Canadian Broadcasting
Corporation, Metro News, and Maclean's Magazine were used with the
search terms "fluoride Calgary" and "fluoridation
Calgary". Again, articles that had at least one comment and had not
been previously identified were added to the list of sources.
Once an exhaustive list of sources had been assembled, a
qualitative judgement was made regarding each source's specific
relevance to fluoridation in Calgary. This was done independently by the
two authors, with disagreements resolved by discussion. Only sources
that pertained to Calgary were used in the next phase of the study.
User comments were extracted from each source. The date of entry of
the comment was recorded (if available), along with the full comment
text. Individual comments were rated on whether they mentioned the
harms/risks of fluoride (yes/no) and on what specific harms/risks were
mentioned. Comments that were in favour of water fluoridation or
negative comments that did not mention any harms/risks were not
considered further. At this stage, it was necessary to develop a working
definition of "harms/risks". We operationalized the term to
include any possible adverse health effects in humans, including harm to
sensitive populations (e.g., children, individuals with existing health
conditions); effects on animals; and effects on the environment (e.g.,
pollution and bio-accumulation). A subset of comments was examined
independently by the two authors to gauge agreement and to refine the
criteria for judgement in order to permit consistency. The two raters
agreed on 94% of the comments (n = 86) from five randomly selected
sources. Harms/ risks were recorded verbatim, sorted into categories of
similar terms, then further combined into groupings of thematically
similar content.
Types of evidence included in online comments about perceived
harms/risks of fluoridation
Next, for those user comments that mentioned the harms/risks of
fluoridation (identified above), we extracted cited sources of evidence.
In other words, we re-examined the comments to determine whether the
user provided any evidence for his/her stated harm/risk. We deliberately
adopted a broad conceptualization of evidence to include anything that
the user identified as support for his/her position (i.e., not just
scientific evidence). We grouped similar types of evidence together and
computed the frequency of occurrence. For scientific papers (one type of
evidence) cited, we retrieved and reviewed the original papers.
Review of scientific literature for a subset of harms/risks
identified in online comments
To consider the broader evidence base, we selected a subset of two
(for feasibility reasons) harms/risks groupings for a structured
literature review: animals, environment and aquatic life (we focused
specifically on aquatic life); and the endocrine system (we focused
specifically on the thyroid gland). We selected these two topics because
we wished to consider both human and nonhuman organisms, and to avoid
duplication of recent published reviews (e.g., cognitive outcomes (16)).
The breadth of the aquatic life search necessitated further focus: we
decided to focus on phytoplankton. Other foci within aquatic life (e.g.,
amphibians) would have been equally good choices. Although scientific
evidence does not resonate with everyone in terms of their views on
fluoridation (i.e., it is not sufficient), it is nonetheless necessary
to maintain an up-to-date knowledge base by reviewing and synthesizing
published literature on specific topics identified by members of the
public as areas of concern. A professional health sciences librarian was
consulted in operationalizing and executing searches. Search details are
provided in Appendix A. For both topics, we first reviewed titles and
abstracts using the inclusion/exclusion criteria described in Appendix
B. All titles and abstracts were reviewed by the first author (PP), and
a subset was independently reviewed by the second author (LM) to assess
and establish consistency.
Papers extracted from both searches were reviewed and summarized.
The following information was extracted into a table: study objective,
rationale, type of study design, study population (e.g., plant species
or human sample), source of fluoride, concentration(s) and exposure
time(s), methods, results and implications for community water
fluoridation. Methodological limitations, as stated by the author, were
also recorded. For each review, a synthesis focused on overall findings,
key methodological limitations and relevance to fluoridation at
recommended levels.
RESULTS
Of the 55 sources identified from the initial search as being
potentially relevant and having comment capacity, 48 (87%) were related
specifically to fluoridation in Calgary. Most sources were published or
posted during 2013 (n = 24;50%), 35% in 2011 (n = 17), 8% in 2012 (n =
4) and 6% in 2014 (n = 3). The degree of relevance was substantive in
46% of cases (n = 22) and constituted only a mention in the remaining
54% (n = 26). Sources were classified as 1) news/newspaper and magazine
articles (n = 24;50%), 2) blogs (n = 9; 19%), 3) public discussion
forums (n = 7; 15%), 4) opinion articles or letters to the editor (n =
4; 8%) and 5) others, including petition, video, website and interview
(n = 4; 8%). Of the news/newspaper and magazine articles, most were
obtained from the National Post (n = 5; 21%) and MacLean's Magazine
(13%). The number of user comments per source ranged from 1 to 824, with
a mean of 69.
Identification of perceived harms/risks of fluoridation mentioned
in online comments
In total, the 48 sources corresponded to 3,330 user comments. Of
these, 356 (10.7%) mentioned the harms/risks of fluoride (based on our
operational definition). Harms/risks were grouped into 56 categories,
which in turn were further combined into 17 thematic groupings. Table 1
shows the 17 thematic groupings, the 56 original categories from which
the groupings were formed, examples and the frequency of occurrence.
Types of evidence included in online comments about perceived
harms/risks of fluoridation
Table 2 presents the types of evidence cited in user comments about
the harms/risks of fluoride, along with examples and frequency of
occurrence. Forty-two percent of comments (n = 176) did not cite any
evidence. Of those comments that did, the most frequent evidence types
were a person viewed as an expert or authority, a generic reference to
research, and a website, including YouTube. Less frequently cited types
included personal experiences, product labels and non-government or
non-profit organizations.
Published literature represented 5.5% of all evidence cited,
corresponding to nine papers. (16-24) These papers are summarized in
Table 3. Overall, the papers have very significant methodological
problems (e.g., no or limited details on methods, limited or unknown
measurement of potentially important confounding variables), and their
relevance to community water fluoridation at recommended concentrations
is limited or unknown.
Review of scientific literature for a subset of harms/risks
identified in online comments
Detailed information about all studies retrieved is available as
supplemental online material. Attributes of studies are summarized in
Table 4. Table 5 shows the correspondence among different units of
fluoride, to permit comparison across studies.
Fluoride and Aquatic Plant Life
The search yielded 2,594 unique citations. After applying inclusion
and exclusion criteria, we arrived at 15 papers for in-depth review.
Four of these were either unavailable in English or could not be
retrieved (via Interlibrary Loan), reducing the final set to 11 papers
(see Table 4 and Supplementary Table 1).
Collectively, the papers may be summed up as follows: at elevated
concentrations (i.e., >2 mg/L) and in some species (e.g., Chlorella
pyrenoidosa), the fluoride ion produces visible toxic effects in algae
and phytoplankton. These effects include inhibition of growth,
photosynthesis, respiration, cell division and protein synthesis, and
reduced cellular ATP (adenosine triphosphate) levels, enzyme activity
(e.g., enolase) and metabolism. However, the toxic effects are variable,
exhibiting fluctuations with fluoride concentration, exposure time,
temperature, water pH, water composition (e.g., the presence of other
ions), water hardness and season. Many of the studies suggest that
fluoride could combine with other constituents present in water (e.g.,
calcium, magnesium), mediating or enhancing toxicity.
In some cases, positive effects of fluoride were observed. There is
minimal growth enhancement observed in some species, suggesting that
fluoride may be a nutritional requirement for these plant forms (e.g.,
Anabaena fertilissima). Further, some species demonstrate resistance to
extreme fluoride levels, hence their use in de-fluoridation experiments
(e.g., Amphidinium carteri).
Overall, levels of fluoride pollution assessed in the studies
reviewed do not seem to pose an immediate threat to the viability and
growth of algae and phytoplankton provided sufficient nutrients are
available. However, an important limitation is that all studies were
carried out in conditions of sufficient nutrients, thus it is important
to consider the implications of nutrient insufficiency on toxicity.
Overall, study quality was poor. Most reviews did not include a
description of the search strategy, inclusion/exclusion criteria or
method of analysis. Frequently, tested fluoride concentrations and
exposure times were not justified, and the rationale for the experiments
was limited or absent. Most studies did not make explicit references to
community water fluoridation.
Fluoride and Thyroid
The initial search of seven databases yielded 955 unique abstracts.
After applying inclusion and exclusion criteria, we arrived at 27 papers
for in-depth review (see Table 4 and Supplementary Table 2).
Collectively, the papers may be summed up as follows:
Human studies Even at more elevated concentrations (e.g., 4.0 ppm),
the fluoride ion did not show toxic effects on the thyroid gland nor did
it clearly affect levels of thyroid hormones. Specifically, few studies
report serum levels of thyroid hormones (T3, T4, thyroid stimulating
hormone) outside the normal range; few studies report any clinical
manifestations of thyroid enlargement (e.g., total thyroid volume is not
different in children exposed to high [e.g., 4.6 mg/L] and normal [e.g.,
0.19 mg/L] fluoride levels);and goitre prevalence does not seem to
correlate with fluoride levels in water.
There were numerous methodological limitations identified in human
studies, relating especially to a lack of control for other variables
(e.g., fluoride consumption in food, presence of other ions and
contaminants in water).
Animal studies Animal models testing extremely high fluoride
concentrations (e.g., 40-500 ppm) report lower thyroid hormone levels
when compared with controls, although these findings are not consistent
across studies or species (i.e., rats, mice and rabbits). Most animal
studies do not translate their findings to humans. The range of fluoride
that showed adverse effects on the thyroid (30-500 ppm) among animals
were in all cases substantially higher than recommended concentrations
for controlled water fluoridation. There were numerous methodological
limitations identified in animal studies, relating especially to a lack
of rationale for fluoride concentrations and mode of administration.
DISCUSSION
Overall, the main conclusions are threefold. First, according to
online comments surrounding fluoridation cessation in Calgary, Alberta,
in 2011, concerns about a wide range of harms/risks of fluoridation were
expressed. These concerns relate to the health of humans (diverse body
systems), the environment, and nonhuman organisms.
Second, a large proportion of comments about harms/risks did not
provide any supporting evidence, and of those that did, the sources of
evidence were diverse, with scientific research infrequently cited. The
nine scientific papers cited were found to have very significant
methodological limitations and at best only very limited relevance to
community water fluoridation at recommended concentrations. Perhaps most
troubling is that, in many cases, information that would permit some
readers to gauge the validity of the study was missing entirely, for
example, studies having no description of how the participants were
sampled, or the absence of a methods section altogether. These are not
minor concerns; they are egregious methodological flaws that make it
very difficult (in some cases impossible) to have confidence in the
reported results.
Third, for the two examples for which we systematically examined
the broader research literature, the evidence likewise did not support
the perceived harms/risks. On the contrary, the scientific evidence
points towards the safety of fluoride at recommended levels (0.7-1.5
mg/L) with respect to these specific harms/risks. Overall, these
findings are consistent with Sandman's concept of
"outrage", whereby perception of risk, for some members of the
public, is influenced by factors other than scientific evidence.
The findings have implications for communication with the public
about fluoridation. First, scientific evidence is only one component of
why some people support or do not support fluoridation strategies.
Communication strategies must accommodate that reality by, for example,
incorporating techniques that are not dismissive of expressed concerns.
Excellent resources are available for this (e.g., the US-based Campaign
for Dental Health, http://ilikemyteeth.org/). Second, to the extent that
members of the public consult the scientific literature, it is essential
that methodological assessment of new studies, including their relevance
to community water fluoridation, is promptly performed and widely
disseminated. There are excellent examples of this as well, such as
appraisals performed by Peel Public Health in the Peel Region of Ontario
(e.g., http://bit.ly/ 1aLhom8).
One limitation of our study is that the comments we examined are
limited to a small segment of the population during a particular time
frame and do not represent those of the public as a whole. They do,
however, resemble the broad cross section of risks/harms identified in
other times and places. (11) Although those who are strongly opposed to
fluoridation and who may thus contribute to online for a are thought to
constitute a small minority of the population, they may have
disproportionate impact on plebiscite outcomes, and thus it is important
to identify, understand and find ways to address their expressed
concerns. Second, because the search was conducted in May 2014, some of
the information posted at the time of the 2011 Calgary plebiscite may no
longer be available online, and unfortunately we do not know the extent
to which this occurred. A third limitation is that for feasibility
reasons our broader literature review focused on only two specific
harms/ risks among the many identified in this study. Although
scientific evidence does not resonate with everyone in terms of
influencing support for/opposition to fluoridation (i.e., it is not
sufficient), it is nonetheless necessary for informed discussion and
decision-making, and thus periodic review and synthesis of existing
research on specific harms/risks and fluoride is important; this was the
reasoning behind our two reviews (for which recent published reviews do
not exist). Fourth, the nature of the evidence base and our review
methods are such that potential biases may be present. Most notably, we
excluded articles published in non-English language (the proportion of
non-English articles on fluoride appears to be non-negligible).
Additionally, we did not perform a formal risk of bias assessment,
opting instead to focus on major methodological limitations and
relevance to community water fluoridation.
Important directions for future research on the subject of public
perceptions and fluoridation include analysis of comments in favour of
fluoridation, including how disagreements play out in online forums;
research into the development and testing of public health communication
messages that reflect our findings here; and ongoing systematic reviews
of research on other perceived harms/risks that showed up in our sample
of comments, such as fluoride's impact on amphibians, issues of the
industrial source of fluoride (e.g., sodium fluorosilicate) and concerns
about arsenic contamination and lead leaching.
REFERENCES
(1.) Spellman, FR. Mathematics Manual for Water and Wastewater
Treatment Plant Operators. Boca Raton, FL: CRC Press, 2004; pp.199-202.
(2.) Health Canada. Summary Report on the Findings of the Oral
Health Component of the Canadian Health Measures Survey, 2007-2009.
Ottawa, ON: Health Canada, 2010.
(3.) Featherstone JD. Prevention and reversal of dental caries:
Role of low level fluoride. Community Dent Oral Epidemiol
1999;27(1):31-40. PMID: 10086924. doi:
10.1111/j.1600-0528.1999.tb01989.x.
(4.) Wolfe J, Ishaque S, Aung YN. The State of Dental Health in
Alberta: A Brief Report. Edmonton, AB: University of Alberta, School of
Public Health, 2013.
(5.) McLaren L, McIntyre L. Drinking Water Fluoridation in Canada:
Review and Synthesis of Published Literature. Prepared for the Public
Health Agency of Canada, Ottawa, 2011.
(6.) Iheozor-Ejiofor Z, Worthington HV, Walsh T, O'Malley L,
Clarkson JE, Macey R, et al. Water fluoridation for the prevention of
dental caries (Review). The Cochrane Library, 2015, Issue 6.
(7.) Understanding public decision-making on community water
fluoridation. J Can Dent Assoc 2013;79:d77. PMID: 23763747.
(8.) Rabb-Waytowich D. Water fluoridation in Canada: Past and
present. J Can Dent Assoc 2009;75:451-54. PMID: 19627654.
(9.) Levy SM. An update on fluorides and fluorosis. J Can Dent
Assoc 2003; 69(5):286-91. PMID: 12734021.
(10.) Public Health England (PHE). Water Fluoridation: Health
Monitoring Report for England 2014. London: Public Health England, 2014.
(11.) Carstairs C, Elder R. Expertise, health, and popular opinion:
Debating water fluoridation, 1945-80. Can Hist Rev 2008;89(3):345-71.
doi: 10.3138/chr.89.3.345.
(12.) Sandman PM. Hazard versus outrage in the public perception of
risk. In: Covello VT, McCallum DB, Pavlova MT (Eds), Effective Risk
Communication: The Role and Responsibility of Government and
Nongovernment Organizations. New York, NY: Plenum, 1989; 45-49.
(13.) "What's Calgary drinking?" The Globe &
Mail [Toronto, Canada] 17 Feb. 2011: A25. Canadian Periodicals Index
Quarterly. Web Available at: http://www.
theglobeandmail.com/globe-debate/whats-calgary-drinking/article566673/
(Accessed October 29, 2015).
(14.) "Calgary's fluoride debate goes public. City
committee will decide next move after late-January meeting". CBC
News, Posted: 10 Jan. 2011. Available at:
http://www.cbc.ca/news/canada/calgary/calgary-s-fluoride-debate-goes-public-1.1015138 (Accessed October 29, 2015).
(15.) McLaren L, Emery JCH, McIntyre L. "Debunking falsehoods
about fluoride". Calgary Sun, 6 Feb. 2011.
(16.) Choi AL, Sun G, Zhang Y, Grandjean P. Developmental fluoride
neurotoxicity: A systematic review and meta-analysis. Environ Health
Perspect 2012;120(10):1362-68. PMID: 22820538. doi: 10.1289/ehp.1104912.
(17.) Duan J, Zhao M, Wang L, Fang D, Wang Y, Wang W. A comparative
analysis of the results of multiple tests in patients with chronic
industrial fluorosis. Guizhou Med J 1995;18(3):179-80.
(18.) Gazzano E, Bergandi L, Riganti C, Aldieri E, Doublier S,
Costamagna C, et al. Fluoride effects: The two faces of Janus. Curr Med
Chem 2010;17(22):2431-41. PMID: 20491635. doi:
10.2174/092986710791698503.
(19.) Grandjean P, Landrigan PJ. Neurobehavioural effects of
developmental toxicity. Lancet Neurol 2014;13(3):330-38. PMID: 24556010.
doi: 10.1016/ S1474-4422(13)70278-3.
(20.) Justus C, Krook LP. Allergy in horses from artificially
fluoridated water. Fluoride 2006;39(2):89-94.
(21.) Sandhu R, Lal H, Kundu ZS, Kharb S. Serum fluoride and sialic
acid levels in osteosarcoma. Biol Trace Elem Res 2011;144(1-3):1-5.
PMID: 19390788. doi: 10. 1007/s12011-009-8382-1.
(22.) Sawan RM, Leite GA, Saraiva MC, Barbosa F, Tanus-Santos JE,
Gerlach RF. Fluoride increases lead concentrations in whole blood and in
calcified tissues from lead-exposed rats. Toxicology 2010;271(1):21-26.
PMID: 20188782. doi: 10.1016/j.tox.2010.02.002.
(23.) Susheela AK, Gupta R, Ganesh K, Brahmankar S, Bhasin S, Gupta
G. Effective interventional approach to control anaemia in pregnant
women. Curr Sci 2010;98(10):1320-30.
(24.) Tang QQ, Du J, Ma HH, Jiang SJ, Zhou XJ. Fluoride and
children's intelligence: A meta-analysis. Biol Trace Elem Res
2008;126(1-3):115-20. PMID: 18695947. doi: 10.1007/s12011-008-8204-x.
Received: February 26, 2015
Accepted: June 5, 2015
Appendix A
Search Strategy: Fluoride and Pollution/Aquatic Life (July 2014)
Databases
Aqualine Biological Abstracts (OVID to 2005) CAB Abstracts
Environment Abstracts Environment Complete Environmental Sciences and
Pollution Management MEDLINE Pollution Abstracts ToxLine Web of Science
Zoological Record
Total abstracts (before de-duplication): 4155 Total abstracts
(after de-duplication): 2594
Search strings and total number of results by database: Aqualine
1. TI (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales) OR AB (algae or aquatic
life* or aquatic mammal* or aquatic organism* or aquatic plants or fish
or salmon or water plants or water pollut* or dolphin* or sharks or tuna
or whales)
2. TI (fluoride* or fluoridation) OR AB (fluoride* or fluoridation)
3. 1 and 2
4. Limit 3 to scholarly peer review journals
Total: 293 results
Biological Abstracts (OVID to 2005)
1. (algae or Aquatic life* or Aquatic mammal* or aquatic organism*
or aquatic plants or Fish or Salmon or Water plants or water
pollut*).tw.
2. (dolphin* or sharks or tuna or whales).tw.
3. 1 or 2
4. fluorid*.tw.
5. 3 and 4
Total: 437 results
CAB Abstracts
1. exp Fishes/
2. exp Aquatic organisms/
3. exp Cetacea/
4. (algae or Aquatic life* or Aquatic mammal* or aquatic organism*
or aquatic plants or Fish or Salmon or Water plants or water
pollut*).tw.
5. (dolphin* or sharks or tuna or whales).tw.
6. water pollution/ or exp water pollution, chemical/
7. exp algae/
8. exp aquatic plants/
9. 1 or 2 or 3 or 4 or 5 or 6 or 7 or 8
10. fluorid*.tw.
11. 9 and 10
Total: 878 results
Environment Abstracts
1. TI (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales)
2. TI (fluoride* or fluoridation)
3. 1 and 2
4. Limit 3 to scholarly peer review journals
Total: 11 results
Environment Complete
1. TI (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales) OR AB (algae or aquatic
life* or aquatic mammal* or aquatic organism* or aquatic plants or fish
or salmon or water plants or water pollut* or dolphin* or sharks or tuna
or whales) OR SU (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales)
2. TI (fluoride* or fluoridation) OR AB (fluoride* or fluoridation)
OR SU (fluoride* or fluoridation)
3. 1 and 2
4. Limit 3 to Scholarly Peer Reviewed Journals
Total: 444 results
Environmental Science and Pollution Management
5. TI (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales) OR AB (algae or aquatic
life* or aquatic mammal* or aquatic organism* or aquatic plants or fish
or salmon or water plants or water pollut* or dolphin* or sharks or tuna
or whales)
6. TI (fluoride* or fluoridation) OR AB (fluoride* or fluoridation)
7. 1 and 2
8. Limit 3 to scholarly peer review journals
Total: 514 results
MEDLINE
1. exp Fishes/
2. exp Aquatic organisms/
3. exp Cetacea/
4. (algae or Aquatic life* or Aquatic mammal* or aquatic organism*
or aquatic plants or Fish or Salmon or Water plants or water
pollut*).tw.
5. (dolphin* or sharks or tuna or whales).tw.
6. water pollution/ or exp water pollution, chemical/
7. 1 or 2 or 3 or 4 or 5 or 6
8. exp Fluorides/ae, to [Adverse Effects, Toxicity]
9. Fluoridation/ae [Adverse Effects]
10. fluorid*.tw.
11. 8 or 9 or 10
12. 7 and 11
Total: 358 results
Pollution Abstracts
1. TI (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales) OR AB (algae or aquatic
life* or aquatic mammal* or aquatic organism* or aquatic plants or fish
or salmon or water plants or water pollut* or dolphin* or sharks or tuna
or whales)
2. TI (fluoride* or fluoridation) OR AB (fluoride* or fluoridation)
3. 1 and 2
4. Limit 3 to scholarly peer review journals
Total: 21 results
ToxLine
1. (algae or aquatic life* or aquatic mammal* or aquatic organism*
or aquatic plants or fish or salmon or water plants or water pollut* or
dolphin* or sharks or tuna or whales)
2. (fluoride* or fluoridation)
3. 1 and 2
4. Limit 3 to scholarly peer review journals
Total: 335 results
Zoological Record
1. (algae or Aquatic life* or Aquatic mammal* or aquatic organism*
or aquatic plants or Fish or Salmon or Water plants or water
pollut*).tw.
2. (dolphin* or sharks or tuna or whales).tw.
3. 1 or 2
4. fluorid*.tw.
5. 3 and 4
Total: 26 results
Web of Science (Science Citation Index and Social Science Citation
Index)
1. SU (algae or aquatic life* or aquatic mammal* or aquatic
organism* or aquatic plants or fish or salmon or water plants or water
pollut* or dolphin* or sharks or tuna or whales)
2. SU (fluoride* or fluoridation)
3. 1 and 2
Total: 838 results
Search Strategy: Fluoride and Thyroid (July 2014)
Databases
MEDLINE PubMED EMBASE Global Health CINAHL ToxLine Web of Science
Total abstracts (before de-duplication): 1616 Total abstracts
(after de-duplication): 955
Search strings and number of results by database: MEDLINE
1. exp Fluorides/ae, to [Adverse Effects, Toxicity]
2. Fluoridation/ae [Adverse Effects]
3. fluorid*.tw.
4. 1 or 2 or 3
5. Thyroid Gland/
6. exp Thyroid Diseases/
7. (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*).tw.
8. 5 or 6 or 7
9. 4 and 8
10. limit 9 to animals
11. limit 9 to (animals and humans)
12. 10 not 11
13. 9 not 12
Total: 144 results
PubMED
1. Fluorides[MeSH] OR Fluoridation[MeSH]
2. fluorid*[tiab]
3. 1 or 2 or 3
4. Thyroid Gland[MeSH]
5. Thyroid Diseases[MeSH]
6. (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*)[tiab]
7. 5 or 6 or 71
8. 4 and 8
Total: 400 results
EMBASE
1. fluoridation/ae [Adverse Drug Reaction]
2. fluoride/ae, to [Adverse Drug Reaction, Drug Toxicity]
3. fluorid*.tw.
4. 1 or 2 or 3
5. exp thyroid gland/
6. exp thyroid disease/
7. (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*).tw.
8. 5 or 6 or 7
9. 4 and 8
Total: 326 results
Global Health
1. exp thyroid gland/
2. exp thyroid disease/
3. (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*).tw.
4. 1 or 2 or 3
5. fluoride/ or fluorides/
6. fluoridation/
7. fluorid*.tw.
8. 5 or 6 or 7
9. 4 and 8
Total: 138 results
CINAHL
1. (MH "Fluoridation") OR (MH "Fluorides+")
2. TI fluorid* OR AB fluorid*
3. 1 or 2
4. (MH "Thyroid Neoplasms") OR (MH "Thyroid
Diseases+") OR (MH "Thyroid Hormones+") OR (MH
"Thyroid Gland") OR (MH "Hypothyroidism+") OR (MH
"Hyperthyroidism +") OR (MH "Graves' Disease+")
OR (MH "Goiter+") OR (MH "Thyrotoxicosis+")
5. TI (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*) OR AB (euthyroid* or goiter*
or goitre* or hyperthyroid* or hypothyroid* or thyroid* or
thyrotoxicos*)
6. 4 or 5
7. 3 and 6
Total: 17 results
Toxline
1. SUfluorid*
2. SU (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*)
3. 1 and 2
Total: 411 results
Web of Science (Science Citation Index)
1. TOPIC fluorid*
2. TOPIC (euthyroid* or goiter* or goitre* or hyperthyroid* or
hypothyroid* or thyroid* or thyrotoxicos*)
3. 1 and 2
Total: 180 results
Appendix B
Inclusion/Exclusion Criteria
A. Inclusion/Exclusion Criteria: Fluoride and Aquatic Life
1. Must include a specific, named harm vs. generic
"pollution" or "contamination" or
"accumulation".
2. Harmful outcome must pertain to aquatic plants and/or
phytoplankton.
3. If study pertains to aquatic animals (e.g., salmon) or
non-aquatic life, such as humans or sheep, exclude.
4. Fluoride vis-a-vis specific, named harm must be primary (vs.
peripheral) focus. For example, if fluoride is one of a number of
compounds being studied, exclude.
5. Focus must be on the direct effect of fluoride on the specific
harm, versus interactive effect. For example, if the focus is how
fluoride interacts with aluminum, exclude.
6. All forms (i.e., ions, compounds) and sources (i.e.,
"natural" and artifical, e.g., industrial waste, controlled
addition at water systems) of fluoride should be considered for
inclusion.
7. If primary focus is processes of defluoridation, exclude.
8. Must be original, empirical research (letters to the editor,
editorials and commentaries are excluded).
B. Inclusion/Exclusion Criteria: Fluoride and Thyroid
1. Fluoride must be primary focus (vs. peripheral). For example, if
fluoride is one of a number of factors being studied, exclude, unless it
is a study of a range of outcomes related to either naturally high
fluoride levels in a region's drinking water or artificially
fluoridated water. Include if fluoride is one of only TWO compounds
under investigation.
2. Focus must be on the direct effect of fluoride on the specific
harm, versus interactive effect.
3. The specific harm must be explicitly related to the thyroid. If
the paper considers the effects of fluoride on multiple organs/systems,
exclude, unless the thyroid is one of only TWO systems being
investigated (e.g., skeleton and thyroid).
4. Must be human science focused (have human application) versus
veterinary sciences or related (e.g., tadpoles).
5. Exclude papers that are mechanism-focused.
6. If the study considers the effects on thyroid hormones, include
if focus is on production; exclude if focus is on circulating hormones
without direct reference to the thyroid or production of the hormones.
7. Must be original, empirical research (letters to the editor,
editorials, and commentaries are excluded).
Paulina C. Podgorny, BHSc, Lindsay McLaren, PhD
Department of Community Health Sciences, University of Calgary,
Calgary, AB
Correspondence: Lindsay McLaren, PhD, Department of Community
Health Sciences, University of Calgary, TRW3, 3280 Hospital Dr. NW,
Calgary, AB T2N 4Z6, Tel: 403-210-9424, E-mail: lmclaren@ucalgary.ca
Acknowledgements: P. Podgorny acknowledges her support through an
O'Brien Centre Summer Studentship (OCSS) from the University of
Calgary. L. McLaren holds an Applied Public Health Chair funded by the
Canadian Institutes of Health Research (Institute of Population and
Public Health; Institute of Musculoskeletal Health and Arthritis), the
Public Health Agency of Canada, and Alberta Innovates--Health Solutions.
We are grateful to Diane Lorenzetti, Research Librarian, Department of
Community Health Sciences, University of Calgary; and to Lorraine Toews,
Librarian, Veterinary Medicine and Bachelor of Health Sciences,
University of Calgary, for their expertise and assistance with the
literature searches.
Conflict of Interest: None to declare.
Table 1. Harms-risks mentioned in online comments pertaining
to community water fluoridation cessation in Calgary,
January 2011-May 2014, ordered by frequency
Thematic Original Example terms Frequency
grouping harm/risk (%) of
category mention
(total
= 639)
Generic: toxic/ Chemicals "Contaminant" 187 (29.3%)
poisonous/ including
chemicals/ build-up in "Deadly poison"
hazardous/ body
contaminant "Toxic"
(including Contaminant
deadly) "May be fatal
Death if swallowed or
inhaled"
Hazardous
"Noxious waste"
Noxious
Poison
Toxic
Generic: Dangerous, "Dangerous 83 (13.0%)
unhealthy/ detrimental substance"
damaging to
health Epidemic "Detrimental
substance"
Harmful
"Harmful side
Multiple effects"
body systems
"Serious
Overexposure abnormalities
of several body
Sick people systems"
Side effects "Health
problems"
Unhealthy
"Linked to
several serious
health
conditions"
Dental, Dental "Staining of 66 (10.3%)
including but fluorosis teeth due to
not limited to mottling of
fluorosis Dental, not tooth enamel"
fluorosis
"Discoloration"
"Rotting"
"Not good for
porcelain caps
as it makes
them crack over
time"
"Weakens teeth"
Behavioural and Attention "Inability to 50 (7.8%)
cognitive deficit concentrate"
hyperactivity
disorder "Lowered IQ" or
"IQ reduction"
Alzheimer's
"Anti-
Anti-depressant depressant
effect on
Autism people"
Depression "Makes you a
slug"
Dyslexia
"Effects on
Energy mental
performance"
IQ
Irritability
Concentration
Generic: Children-- "Harm to young 38 (5.9%)
children, generic children"
elderly
Elderly people "Overexposure
--generic in formula-fed
infants"
"The elderly"
"Affects
seniors"
"Babies"
Animals, Animals "Spinal 37 (5.8%)
environment and Environment collapse in
aquatic life guppies"
"Cattle dropped
dead"
"Harms salmon
and other
aquatic life"
"Harm to the
downstream
environment"
"Damaging
environmental
pollutant"
Bones and Skeletal "Degenerative 36 (5.6%)
skeleton fluorosis problems in
bone, bone
Bone problems tissue"
(break,
fracture) "Broken hips
from brittle
Arthritis bones"
"Painful and
debilitating
fluorosis in
the joints"
Arthritis as
"subclinical
skeletal
fluorosis"
"Affects
skeleton"
Endocrine Pineal gland "Thyroid 36 (5.6%)
system suppressant"
Thyroid
"Goitre
development"
"Pineal gland
damage"
"Suppresses
thyroid by
competing with
iodine for
absorption in
the thyroid"
"Overactive
thyroid"
Cancer Cancer "Rats started 34 (5.3%)
to develop
small tumours
in their
brains ...
tumours
developing in
their stomach
lining"
"Bladder
cancer"
"Bone cancer"
"Carcinogenicity"
"Osteosarcoma"
Brain and Brain and CNS "Destroys the 24 (3.8%)
central nervous brain"
system (CNS) Neurotoxin
"Calcinates
parts of the
brain"
"Abnormal
development of
the central
nervous system
in fetuses and
young children"
"Neurotoxin
which impairs
brain function"
"Central
nervous system
effects"
Urinary system Bladder "Those with 23 (3.6%)
kidney
Dehydration impairment"
Kidney disease "Anyone with
kidney stones"
"Stress on the
kidneys"
"Serious
bladder
problems and
surgeries"
"People on
kidney
dialysis"
Immune system Allergy "The immune 8 (1.3%)
compromised"
Immune system
"Allergic
Irritation reactions"
Oxidative "Causes
stress irritation to
skin, eyes"
Sensitivity
"Causes
Ulcers oxidative
stress by
interfering
with the body's
defence
mechanisms
against
reactive oxygen
species"
"Mouth ulcers"
Digestive Digestive "Upset stomach" 6 (0.9%)
system system
"Digestive
Liver systems of
fluoride
poisoning"
"Stomach
problems"
"Not good for
your liver"
"Nausea"
Others Diabetes "People with 4 (0.6%)
diabetes" or
Genetic "Diabetics"
Hair "Genetic
damage"
"Hair loss"
Circulatory Cardiovascular "Coronary 3 (0.5%)
system system artery disease"
"Scarring
arterial walls"
"Affects
circulatory
system"
"Harmful to
many arteries"
"Affects
heart"
Respiratory Respiratory "Chronic 2 (0.3%)
system and cough"
related
"Affects
respiratory
system"
Pregnancy and Pregnancy and "Sudden infant 2 (0.3%)
related related deaths"
"Anemia in
pregnant women"
"Premature
births"
"Low baby birth
weight"
Table 2. Types of evidence cited in online comments, ordered
by frequency
Type of evidence Examples and/or Frequency (%) of
sample quotes mention (total =
416)
None (no evidence) N/A 176 (42.3%)
Person viewed as an "Dr. James Beck"
expert or authority,
including personal "Christopher Bryson
expertise and (journalist)"
credentials
"14 Nobel prize
winners in either 53 (12.7%)
medicine or
chemistry"
"I am a practicing
dental hygienist"
"I'm a nutritionist
that practices
alternative
medicine"
Generic reference to "Feel free to ask 30 (7.2%)
research for sources"
"Read the facts
about what happens
to kids who get too
much fluoride before
the age of 8"
"Numerous scientific
studies"
"According to new
research"
"More and more
science is showing"
Website, including http://slw eb.org/ 30 (7.2%)
YouTube bibliography.html
("A Bibliography
of Scientific
Literature on
Fluoride")
http://
www.nofluoride.com
/presentations/
Nobel%20Prize%20
Winners.pdf ("14
Nobel Prize
Winners who
object to
fluoridation")
www.fluoridealert
.org (Website of
The Fluoride
Action Network)
http://en.wikipedia
.org/wiki/Dental_
fluorosis
(Wikipedia page
for dental
fluorosis)
http://cof-cof.ca/
convincing-canadian
-studies-
demonstrating-water
-fluoridations-
questionable-
merit/ (A list
of "Convincing
Canadian studies
demonstrating water
fluoridation's
questionable
merit")
Personal experience "We have lost 8 25 (6.0%)
horses and 4 dogs
from the
consumption,
accumulation and
systemic effects of
this product"
"It destroyed my
thyroid"
"I've started to
lose a lot of hair
... my thyroid
started acting up
and I developed a
goitre"
"I've been fighting
health problems"
"I don't use tap
water for the
guppies either, it
was causing their
spines to collapse"
Government report or "Food and Drug Act" 23 (5.5%)
organization,
including government "The Safe Drinking
acts and regulations Water Act (2002)"
"The Ontario Safe
Drinking Water Act,
Section 19, in
effect January 2013"
National Research
Council
"The Canadian Health
Measures Survey
(CHMS) released data
..."
Study or article in "Sawan, et al. 23 (5.5%) *
peer-reviewed (Toxicology 2/2010):
journal Water fluoride
chemicals boost lead
absorption in lab
animals' bones,
teeth and blood"
"Tang el al.,
"Fluoride and
Children's
Intelligence: A
Meta-analysis" in
Biological Trace
Element Research"
My own research/ "I have done 17 (4.1%)
reading extensive research
on fluoride"
"I read an article"
"I have read
reports"
Product label "If you look at the 13 (3.1%)
bag labels Sodium
Fluoride you will
see the skull and
cross bones"
"Warning labels on
toothpaste"
"Material Safety
Data Sheet"
Documentary, "Christopher 13 (3.1%)
magazine, or book Bryson's 'The
Fluoride Deception'"
The Case Against
Fluoride
"Book published in
1961, The
Fluoridation
Experiment, by
Exner, Waldbott &
Rorty"
"Time magazine
listed fluoride as
one of the 'Top Ten
Common Household
Toxins' and
described fluoride
as both 'neurotoxic
and potentially
tumorigenic if
swallowed.'"
NGO/non-profit The Council of 11 (2.6%)
organization Canadians (Windsor
Chapter)
Sierra Club
Columbia
Riverkeepers
The Canadian
Association of
Physicians for the
Environment
The National Kidney
Foundation
Newspaper "Editorial that 2 (0.5%)
appeared in the
Windsor Star"
"Howard University's
student newspaper,
The Hilltop"
* Corresponds to 9 separate published articles, some of
which were mentioned multiple times.
Table 3. Summary of published scientific papers * cited in
online comments
Citation (#) Synopsis Key issues/concerns
Choi et al. Systematically Quality of original
(16) reviewed research on studies is quite poor
fluoride and (e.g., information on
neuro-developmental child's sex and
delays published parental education was
between 1980 and 2011, not reported in >80%
including studies from of studies, and only
rural China that 7% [n = 2] of studies
examine naturally reported household
occurring high levels income; most reports
of fluoride. Studies were fairly brief and
contained high and complete information
reference exposure on covariates was not
groups (final n = 27; available; most
2 from Iran and the studies did not report
rest from China). age adjustment of the
Overall results cognitive test
support association scores). All original
between high fluoride studies appear to be
exposure and lower cross-sectional
intelligence (based on comparisons of
standardized mortality fluoridated and
ratio, pooled risk non-fluoridated
ratio). Finding was groups. Fluoride
robust to different concentrations in the
study exclusions. high exposure group
were in most cases
higher than
recommended (0.7 ppm)
and maximum (1.5 ppm)
levels: range >2 to 11
ppm.
Duan et al. Various tests (i.e., Paper was translated
(17) cognitive ability, from Chinese by the
electroencephalograph, Fluoride Action
neurological history Network. No
taking and physical information on how
examinations) were participants were
administered among sampled/selected
three groups of within each group.
individuals: 1) n =72 Though authors report
men with chronic that economic status,
industrial fluorosis lifestyle habits and
who worked or had other factors were
worked in the similar across the
electrolysis workroom groups, no data are
at an aluminum presented, and there
production facility; is no information on
2) n = 43 men who had how these were
worked in same measured nor what
environment for less "lifestyle habits" and
time and whose "other factors"
condition did not meet entail. Limited
the diagnosis for information is
industrial fluorosis; provided on the tests
and 3) n = 42 healthy and what the results
persons. Economic mean (e.g., from the
status, lifestyle electroencephalogram,
habits and other the proportion
factors were similar moderately abnormal
across groups. Across and mildly abnormal
tests, the worst are reported for each
outcomes were observed group, but it is not
in group A (longest clear what these
exposure) followed by categories mean or how
group B (shorter they were assigned).
exposure), and the Whether the findings
best results were in have relevance to
group C (healthy fluoridated drinking
group). Exposure was water and to what
confirmed by air extent is unclear.
quality tests in the
facility and from
fingernail samples.
Gazzano et Review article (134 No methods section; it
al. (18) references) anchored is unclear how the
in the observation authors selected the
that fluoride's studies reviewed.
behaviour in the human Article is very
organism makes it a technical, therefore
classic example of a not accessible to a
double-edged sword. non-expert reader.
The rationale for the
article appears to be
the proposed insertion
of fluoride in the
preparation of
biomaterials to
improve their
integration in the
bone, which demands
understanding of the
safety of fluoride in
terms of prolonged
exposure to living
tissue. The review
covers the following
areas: 1) fluoride
metabolism and types
of exposure; 2)
mechanisms of fluoride
action on dental
caries onset; 3)
fluoride application
in caries prevention;
4) effects of fluoride
on bone; 5) acute and
chronic effects of
fluoride; 6)
activation of G
proteins and kinases
and inhibition of
phosphatases; 7)
fluoride inhibition of
many other enzymes;
and 8) fluoride and
oxidative stress.
Concludes by
presenting a model for
"Is there a unifying
hypothesis for
fluoride effects?"
Grandjean & Review (115 Search-selection
Landrigan (19) references) that is an methods are only
update of a 2006 briefly described.
review of the Because the
developmental identification of
neurotoxicity of fluoride as a newly
industrial chemicals. recognized
The 2006 report developmental
identified five neurotoxicant is based
industrial chemicals entirely on Choi, (16)
that could be reliably this paper suffers
classified as from the same
neurodevelopmental limitations as above
toxicants: lead, in terms of the low-
methylmercury, unknown quality of the
arsenic, original studies. The
polychlorinated section on "newly
biphenyls and toluene. recognized
The authors are developmental
concerned that neurotoxicants" begins
subclinical toxicity with a paragraph about
may be widespread "powerful
before it is realized epidemiological
that concentrations methods" such as
thought to be safe are prospective birth
shown, by cohort studies, which
epidemiological gives the misleading
research, to be too impression that the
high. They also cite information that
examples of early follows is based on
warning signs of those methods. The
subclinical studies in the Choi
neurotoxicity being paper, (16) as noted
ignored or dismissed. above, are all cross-
Fluoride is recognized sectional, mostly do
as one of the "newly not include any
recognized covariate information
developmental and pertain to higher
neurotoxicants". This than recommended
is based entirely on fluoride levels.
the Choi (16) paper
above.
Justus & Authors build on The paper is an
Krook (20) another paper recently account of a personal
published in the same experience; as such,
journal, which it lacks the
demonstrated fluoride systematic nature of
poisoning in horses rigorous research, and
that consumed thus it is more
artificially difficult to rule out
fluoridated water. alternative
This paper focuses on explanations.
allergy as another
expression of
fluorosis in horses.
The horses were not
likely exposed to
other sources of
fluoride. Over the
years, 2 of 11 horses
exposed to the water
developed allergy
(skin lesions), and
the two cases are
presented. In the
first horse, for
example, the lesions
were reduced when the
horse consumed snow
instead of fluoridated
water and disappeared
when it consumed water
from a different
source. Eventually,
the horse was taken
off fluoridated water
altogether and the
lesions ceased
entirely.
Sandhu et al. The study aimed to The age/and sex/
(21) examine serum matching is only
fluoride, among other mentioned in the
things, in 25 abstract (not in the
osteosarcoma patients methods section). No
as well as age- and information about how
sex-matched controls the individuals were
with 1) bone-forming sampled/selected. No
tumours other than other information
osteosarcoma (n = 25) about the three groups
and 2) musculoskeletal (covariates) to permit
pain (n = 25). Found assessment of how
that serum fluoride similar/different they
levels were were on other
significantly higher variables. Conclusion
in the osteosarcoma is thus overstated:
group than in the two "this report proves a
control groups. The link between raised
authors acknowledged fluoride levels in
studies that show a serum and
link between fluoride osteosarcoma".
in drinking water and Implications for
osteosarcoma as well fluoridated drinking
as those that did not water at recommended
show a link. levels are unclear.
Sawan et al. Authors aimed to test The fluoride
(22) whether administration concentration far
of fluorosilicic acid exceeds recommended
could increase blood (0.7 mg/L) and maximum
lead content and (1.5 mg/L) levels for
mineralized tissue drinking water.
lead concentration in Relevance of findings
rats exposed to low to community water
levels of lead from fluoridation is
the beginning of minimal, if any.
gestation
(silicofluoride is the
fluoride compound used
most commonly for
fluoridated water in
the US, Canada and
other countries). The
fluoride concentration
for the control and
lead-only groups was 1
mg/L; for the fluoride
and fluoride + lead
group it was 100 mg/L.
The authors note that
this fluoride
concentration produces
plasma fluoride levels
that are comparable to
those commonly found
in humans chronically
exposed to 8 mg/L in
drinking water (which
far exceeds
recommended and
maximum levels).
Higher blood lead
concentrations were
reported in the
fluoride + lead group
compared with the
lead-only group, and
lead concentrations in
calcified tissues were
significantly higher
in the fluoride + lead
group than in the
lead-only group. No
significant
differences in
fluoride
concentrations in
calcified tissues were
found between these
groups.
Susheela et Article examined The paper is poorly
al. (23) (among other things) written/organized, so
whether, among anemic is difficult to
pregnant women with follow. Unclear
urinary fluoride whether the effect is
beyond 1.0 mg/L, an attributable to the
intervention to reduce reduction in fluoride,
fluoride intake the improved nutrition
reduced pre-term or a combination of
births and low birth the two. Although
weight. The covariate data were
intervention included collected, it does not
counselling on how to appear that the
avoid fluoride in authors examined
water and food. whether results could
Eligible women were be explained by
randomly assigned to covariates (though
intervention vs. random allocation is a
control groups. strength).
Information on
confounding factors
was gathered: diet,
economic status,
literacy status,
employment status,
first pregnancy,
miscarriage and other
problems, other
ailments, and use of
folic acid and iron
supplements. The
intervention group,
compared with the
control group, had
higher (better)
hemoglobin and higher
birth weight/lower%
low birth weight.
Tang et al. A systematic review of No information at all
(24) studies from China, on covariates/
written in English or confounders in
Chinese, on the original studies or
association between any other
fluoride and methodological detail
intelligence/IQ, of the original
published between 1988 studies.
and 2008 (the "earlier
review" cited by Choi
(16). Among the 16
included "case
control" studies, the
authors found that
children in
fluoridated areas had
increased risk of
lower IQ
(meta-analysis,
sensitivity analyses).
* All studies are published in peer-reviewed journals.
Table 4. Attributes of the final set of papers from the
aquatic plants/phytoplankton (n = 11) and thyroid
(n = 27) literature searches (see Supplementary Tables
1 and 2 for details of individual studies)
Topic of review Publication Main countries
years (range) of origin
Fluoride and 1962-1999 (55%) Canada (45%)
aquatic plants/ 2000-2011 (45%) India (18%)
phytoplankton Other (36%)
Fluoride and 1960-1999 (56%) India (30%)
thyroid 2000-2014 (44%) Tunisia (11%)
China (11%)
United States (7%)
Switzerland (7%)
Turkey (7%)
Other (26%)
Topic of review Study type Fluoride forms
administered/
tested
Fluoride and Experimental (55%) Sodium fluoride
aquatic plants/ Review (36%) (NaF), hydrogen
phytoplankton Observational (9%) fluoride (HF)
and ammonium
fluoride
(N[H.sub.4]F)
(only NaF is
commonly used
for water
fluoridation).
Fluoride and Observational (44%) Sodium fluoride
thyroid Experimental (48%) (NaF) Naturally
Review (8%) occurring
fluoride (e.g.,
studies of
children in
areas of high
naturally
occurring
fluoride in the
water).
Topic of review Levels/ Measured
concentration parameters
of fluoride and
exposure times
Fluoride and 0 to 1900 mg/L Growth
aquatic plants/ Exposure times (measured as
phytoplankton ranged from hours cell number
(minimum 5) to and/or
days (maximum absorbance),
36). oxygen
exchange, ATP
levels,
chlorophyll
content, enzyme
activity (i.e.,
carbonic
anhydrase) and
respiratory
activity.
Fluoride and 0 to 500 ppm Thyroid volume,
thyroid thyroid weight,
thyroid hormone
levels in serum
(T3, T4, and
thyroid
stimulating
hormone),
clinical
thyroid
enlargement and
goitre
prevalence.
Table 5. Unit conversion chart (for fluoride concentrations)
Standard Equivalent Recommended fluoride concentration
unit unit in drinking water (converted)
1 mg/L 1 ppm 0.7-1.5 ppm
0.05 mM 0.035 mM-0.075 mM
50 [micro]M 35 [micro]M-75 [micro]M