WAPF WELLINGTON TOP 5 MOST POPULAR BLOG POSTS THIS MONTH (Scroll down to see the latest posts)

Wednesday, 26 February 2025

Is stevia safe?

Stevia is one of those foods that seems to taste delicious to some people but nasty to others. I like the taste of it, and because I never eat any sugar or any other sweeteners, I hoped it was OK to consume stevia in moderation. It is a natural plant food rather than a refined chemical like most sweeteners, but on the other hand it has had some bad press. 


So when I read this very well researched article in a WAPF journal I wasn't very pleased to hear all this bad news about one of my few remaining indulgences.  
 
As far as I know, my daily use of a small amount of stevia wasn't causing any bad side effects, but there are many articles that are very negative about stevia, so I reluctantly stopped using it. I missed it for a few weeks but soon got used to the taste of foods without it.
 
After not having any for six months I started having it from time to time again and didn't notice any negative effects. So I'm open minded about stevia, but personally, I like it, and haven't noticed any adverse effects from it.


This is the bad side to stevia all laid out in full:

"This article provides an abbreviated overview of the research on stevia and its detrimental effects on various body systems, which I explain at greater length in my book. I feel sure that anyone who understands the risks will no longer want to consume stevia or feel safe doing so" - MARCH 5, 2024 BY JOCELIN WHITAKER





Sunday, 23 February 2025

Vitamin C

 

Megadose Vitamin C therapy

A book that provides a great introduction is “Vitamin C the Real Story” by Steve Hickey and Andrew Saul

Another really good book is “Primal Panacea” by Thomas Levy

An excellent one of the original books by Linus Pauling is “How to live longer and feel better” (1986)

More information is also available from www.vitaminc.co.nz


Ways to take Vitamin C

Liposomal Vit C is best if taking large 6 – 20+ gram daily doses

Nature Foods sells NZLF Liposomal Vit C for $38 for 30 sachets each containing 1000mg Vitamin C.

https://www.naturefoods.co.nz/supplements/vitamins/liposomal-vitamin-c

The newer Micro Liposomal Vitamin C is also available.

This is more convenient to take than the regular liposmal vitamin C – a liquid rather than a gel, but it is also more expensive.

https://www.naturefoods.co.nz/supplements/vitamins/quicksilver-c

www.naturefoods.co.nz

Powders are really only suitable for small maintenance doses of up to 1- 4 grams per day – for mega dosing we recommend taking Liposamal or Microsomal Vit C.

(Many of the colourful pictures on this page are optical microscopy images of Vitamin C)


Liposamal Vitamin C dosage – to fart tolerance

    I have found this works well for minor illnesses like colds, but I made this up myself and some people may say it’s a load of bollocks

  Cut out all the other types of Vit C

  Start with 6x 1gram doses of Liposomal spread through the day with one in the middle of the night

  (6 grams is too low for pretty much everyone but it’s a safe starting point)

  Add 2 extra grams a day until you start to fart a bit.

If you start to fart a lot back off until it’s only occasional farting

(Vit C farts are mild and odourless so it’s not as bad as it sounds )

  As the dose becomes larger it’s easier to take two grams at a time.

I have found 12 grams a day works well to rapidly fix problems such as colds

 


Have we been going backwards with knowledge of Vitamin C for the past 40 years like we have with cars?

1972 – Valiant Charger in “Vitamin C Orange” – awesome!

2012 – Smart Car in “snot green” – less than awesome


This video clip uses a few gratuitous arse shots to up its ranking, but the treatment works brilliantly


Vitamin C – a cure for Ebola

Steve Hickey PhD, Hilary Roberts PhD, and Damien Downing MBBS, MSB.

Vitamin C is the primary antioxidant in the diet. Most people do not take enough to be healthy. While this is true of many nutrients, vitamin C is a special case.

Ignore governments telling you that you only need about 100 mg a day and can get this amount from food. The required amount of vitamin C varies your state of health. A normal adult in perfect health may need only a small intake, say 500 mg per day, but more is needed when someone is even slightly under the weather.

Similarly, to prevent illness, the intake needs to be increased. The intake for an otherwise healthy person to have a reasonable chance of avoiding a common cold is in the region of 8-10 grams (8,000-10,000 mg) a day.

This is about ten times what corporate medicine has tested in their trials on vitamin C and the common cold. Ten grams (10,000 mg) is the minimum pharmacological intake; it may help if you have a slight sore throat but more (much more) may be needed.

To get rid of a common cold, you may need anything from 20 to 60 grams (60,000 mg) a day. With influenza the need might be for 100 grams (100,000 mg) a day. Since it varies from person to person, and from illness to illness, the only way to find out is to experiment for yourself.

Dynamic flow – The problem with oral intakes is that healthy people do not absorb vitamin C well due to something Dr Robert Cathcart called bowel tolerance. Take too much of the vitamin in a single dose and it will cause loose stools.

In good health, a person might be able to take a couple of grams at a time without this problem. Strangely, when a person becomes sick they can take far more without this side effect: as much as 20-100+ grams a day, in divided doses.

High dose vitamin C has a short half-life in the body. The half-life is the time for the level in the blood plasma to fall back to half its concentration. Until recently, some people claimed that the half-life of vitamin C was several weeks.

We have shown that this long half-life applies only to very low doses. By contrast, the half-life for high blood levels is only half an hour. This short half-life means that for high dose vitamin C the period between doses needs to be short – a few hours at most.

The aim is to achieve dynamic flow, to get vitamin C flowing continuously through the body. Dynamic flow requires multiple high doses taken throughout the day. When separated in time, each dose is absorbed independently. Two doses of 3 grams, taken 12 hours apart, are absorbed better than 6 grams taken all at once.

Multiple large doses, say 3 grams four times a day, produce a steady flow of the vitamin from the gut, into the bloodstream and out, via the urine. Some of the intake is not absorbed into the blood and stays in the gut, as a reserve against the early onset of illness.

As illness begins, the body pulls in this “excess” to help fight the virus. The idea behind dynamic flow is that the body is kept in a reduced (antioxidant) state, using high doses. There is always vitamin C available, to refresh the body and other antioxidants.

Each vitamin C molecule (ascorbic acid) has two antioxidant electrons, which it can donate to protect the body. It then becomes oxidized to dehydroascorbate (DHA). This oxidized molecule is then excreted, so the body has gained two antioxidant electrons.

The kidneys reabsorb vitamin C, but not DHA; the vitamin C molecule is absorbed, used up, and then the oxidized form is thrown out with the rubbish. The effectiveness of vitamin C is not directly proportional to the dose; it is non-linear.

There is a threshold above which vitamin C becomes highly effective. Below this level, the effect is small; above it, the effect is dramatic. The problem is that no-one can tell you in advance what intake of vitamin C you need. The solution is to take more – more than you think necessary, more than you consider reasonable. The mantra is dose, dose, dose.

Sugar interferes with the uptake of vitamin C. If you are using vitamin C to combat a viral infection do not eat any sugar or carbohydrates (long chain sugars) or the vitamin C will not be absorbed properly. We stress that this means no sugar and no carbs, at all.

Orthomolecular Medicine News Service


UNIQUE FUNCTION OF VITAMIN C – Dr. Robert F. Cathcart, M.D.

Vitamin C is a reducing substance, an electron donor. When vitamin C donates its two high-energy electrons to scavenge free radicals, much of the resulting dehydroascorbate is rereduced to vitamin C and therefore used repeatedly.

Conventional wisdom is correct in that only small amounts of vitamin C are necessary for this function because of its repeated use. The point missed is that the limiting part in nonenzymatic free radical scavenging is the rate at which extra high-energy electrons are provided through NADH to rereduce the vitamin C and other free radical scavengers.

When ill, free radicals are formed at a rate faster than the high-energy electrons are made available. Doses of vitamin C as large as 1 to 10 grams per 24 hours do only limited good. However, when ascorbate is used in massive amounts, such as 30 to 200+ grams per 24 hours, these amounts directly provide the electrons necessary to quench the free radicals of almost any inflammation.

Additionally, in high concentrations ascorbate reduces NAD(P)H and therefore can provide the high-energy electrons necessary to reduce the molecular oxygen used in the respiratory burst of phagocytes. In these functions, the ascorbate part is mostly wasted but the necessary high-energy electrons are provided in large amounts.

DEFINITION AND QUALIFICATION

In this paper, the words, vitamin C, will refer to the substance C6H8O6 used in tiny doses as a vitamin and an electron carrier. The word, ascorbate, will mean the same substance but when used in massive amounts for its high-energy electrons themselves.

This paper is not meant to be an exhaustive review of the subjects of oxidation-reduction reactions, free radical scavenging, electron-transport-chains, or oxidative phosphorylation, etc. Many of the biochemical processes are deliberately simplified. Some intermediate steps are omitted. Certain generalizations are made so that the importance of a very simple but overlooked idea can be described in terms a non-biochemist can understand.

The overlooked idea is that massive doses of ascorbate can actually be the source of high-energy electrons used in the process of free radical scavenging and not just an electron carrier used repeatedly in an electron-transport-chain resulting in free radical scavenging.

INTRODUCTION

Clinically, a few physicians have found massive doses of ascorbate to be effective in the treatment of a wide variety of diseases. It was apparent to those using ascorbate in these doses that there is some physiologic or pharmacologic action much different from what might be expected of a mere vitamin. Nevertheless, most physicians remained critical of these treatments and remained convinced that the usefulness of ascorbate is only as vitamin C.

Many had recognized that one vitamin C function is as a free radical scavenger. In this function, vitamin C donates high-energy electrons to neutralize free radicals and in the process becomes DHA (dehydroascorbate). DHA is either further metabolized, releasing more electrons, or is rereduced back to vitamin C to be used over and over again. This regeneration and repeated use of the vitamin has led to the thought that it does not take much to do its functions.

Other nonenzymatic free radical scavengers such as glutathione and vitamin E function in a similar manner. The purpose of taking the nutrients making up the free radical scavengers is ordinarily to replace the small percentage inadvertently lost. Much of the original work with large amounts of ascorbate was done by Klenner who found that most viral diseases could be cured by intravenous sodium ascorbate in amounts up to 200 grams per 24 hours.

Irwin Stone pointed out the potential of ascorbate in the treatment of many diseases, the inability of humans to synthesize ascorbate, and the resultant condition hypoascorbemia. Linus Pauling reviewed the literature on vitamin C, particularly its usefulness in the prevention and treatment of the common cold and the flu.

Ewan Cameron in association with Pauling described the usefulness of ascorbate in the treatment of cancer. In 1970 I noted an increasing bowel tolerance to oral ascorbic acid with illness. In 1984 I wrote, “Based on my experience with over 11,000 patients during the past 14 years, it has been my consistent observation that the amount of ascorbic acid dissolved in water which a patient, tolerant to ascorbic acid, can ingest orally without producing diarrhea, increases considerably somewhat proportionately with the “toxicity” of his illness.

A person who can tolerate orally 10 to 15 grams of ascorbic acid per 24 hours when well, might be able to tolerate 30 to 60 grams per 24 hours if he has a mild cold, 100 grams with a severe cold, 150 grams with influenza, and 200 grams per 24 hours with mononucleosis or viral pneumonia.

The clinical symptoms of these diseases and other conditions previously described, are markedly ameliorated only as bowel tolerance dose levels (the amount that almost, but not quite, causes diarrhea) are approached.

This amelioration of symptoms at a high dosage threshold combined with the knowledge that ascorbate functions as a reducing substance suggested that the beneficial effect was achieved only when the redox couple, ascorbate/dehydroascorbate, became reducing in the tissues affected by the disease. It is a characteristic of oxidation-reduction reactions that their redox potential is determined by the logarithm of the concentrations of the substances and certain constants.

The logarithmic effect would explain the threshold; the redox potential would suddenly become reducing in the diseased tissues only when a large amount of ascorbate was forced into those tissues sufficient to neutralize most of the oxidized materials in those tissues.

FREE RADICAL SCAVENGING

Radicals are molecules that have lost an electron. When a radical escapes its normal location, it becomes a free radical. These free radicals are very reactive and will seize electrons from adjacent molecules.

Inflammations whether due to infectious diseases, autoimmune diseases, allergies, trauma, surgery, burns, or toxins involve free radicals. Cells injured by free radicals will spill free radicals onto adjacent cells injuring those cells and generating more free radicals, etc.

The body must confine these free radical cascades with free radical scavengers. Some free radicals spontaneously decay and others are destroyed by enzymatic free radical scavengers such as superoxide dismutase and catalase that act on free radicals in such a way that they neutralize themselves without the addition of extra electrons.

The remainder must be destroyed by the high-energy electrons carried by the nonenzymatic free radical scavengers. Free radicals that escape all the above mechanisms cause symptoms and damage. It is helpful to remember through all the following descriptions that technically it is the high-energy electron that is neutralizing the free radical, not the free radical scavenger. The free radical scavenger carries the high-energy electron that does the neutralizing.

HIGH-ENERGY ELECTRONS THE LIMITING FACTOR

The energy of the electrons which neutralize free radicals comes ultimately, like all energy used by living things on Earth, from the Sun. Plants store this energy by photosynthesis in carbohydrates, fats, and proteins which are then eaten by animals.

As animals metabolize these substances, this energy is past from one molecule to another in the form of high-energy electrons which often, but not always, are in association with hydrogens. Together with a high-energy electron, one such hydrogen can be called a hydride anion. As glucose is metabolized, NAD+ (nicotinamide adenine dinucleotide) is reduced to NADH (the bolded H is to emphasize the included high-energy electron).

The high-energy electron in the hydride anion (H) is added to the NAD+. The most critical but generally unrecognized fact here is that NAD+ can be reduced to NADH only at a limited rate by the addition of the hydride anion with its high-energy electron derived from the metabolism of carbohydrates, fats, or proteins.

Therefore, this NADH is not without cost. Moreover, the energy it carries must be shared among several other critical functions. Most must be used in the process of oxidative phosphorylation to make ATP (adenosine triphosphate) which is used as a source of energy by the various tissues of the body.

When phagocytes engulf pathogens into its vacuoles, NADPH (nicotinamide dinucleotide diphosphate, reduced form) provides the high-energy electrons the phagocytes need to make the oxidizing substances (radicals) with which they kill various pathogens. The process of making the necessary oxidizing substances is called the respiratory burst.

Paradoxically, the first oxidizing substance, superoxide, (O2+), in the respiratory burst is made by the reduction of molecular oxygen (O2) by NADPH. NADP+ is rereduced back to NADPH in the hexosemonophosphate shunt. Glucose is metabolized for the source of the high-energy electron.

This process is also rate-limited and the glucose comes from the metabolism of carbohydrates, fats, and proteins. Therefore, NADH and NADPH have a common source of energy and can be made available only at some limited rate.

Remaining NAD(P)H can be used by the body in regenerating free radical scavengers so that the body may protect itself from free radicals. As NAD(P)H is used in these various processes, it gives up the hydride anion with its extra high-energy electron and becomes NAD(P)+ again. When the limited rate of availability of these hydride anions is exceeded by the formation of free radicals, then symptoms and damage caused by the free radicals occur.

RESPIRATORY BURST LIMITED BY ACCUMULATION OF FREE RADICALS

As these high-energy electrons are used up within the phagocytes, the phagocytes are unable to produce more oxidizing substances within their vacuoles to kill pathogens. Some of the previously made oxidizing substances leak from within the vacuoles into the cytoplasm thereby becoming free radicals.

With the exhaustion of the high-energy electrons, the nonenzymatic free radical scavengers cannot be rereduced. The free radicals damage the phagocytes and interfere with phagocytosis. The phagocytes bog down in their own oxidizing substances.

REDUCED GLUTATHIONE

To understand the unusual function of massive doses of ascorbate, let us follow the most important pathway whereby the extra electrons are passed off to the free radicals thereby neutralizing them. Follow the high-energy electron in the hydride anion through all this process.

Certain nutrients that could be limiting factors in all this will be mentioned along the way. NAD(P)H reduces oxidized flavin adenine dinucleotide (FAD+), to reduced flavin adenine dinucleotide (FADH2), and becomes NAD(P)+ again. FADH2 reduces oxidized glutathione (GSSG) to reduced glutathione (GSH). (Part of NAD(P)H is from vitamin B3, and part of FADH2 is from vitamin B2).

The high-energy electrons of reduced glutathione (GSH) can directly reduce some free radicals. But also, some reduces dehydroascorbate back to ascorbate. In the process the GSH is oxidized back to GSSG. Two hydride anions are added to the dehydroascorbate reducing it back to vitamin C. (The enzyme glutathione peroxidase and its coenzyme selenium catalyze these reactions).

Ascorbate (C6H8O6 or C6H6O6H2, the bolded and separated H2 is to emphasize the hydrogens containing the high-energy electrons) differs from dehydroascorbate (C6H6O6) in that it has two extra hydrogen atoms with two high-energy electrons in its molecular structure which it can donate to reduce free radicals. The high-energy electrons of ascorbate, C6H6O6H2, can directly quench free radicals. But some may reduce tocopheryl quinone (an oxidized form of vitamin E) back to à-tocopherol (vitamin E).

Some high-energy electrons are passed to the à-tocopherol and then quench free radicals. The point I want to emphasize is that these free radical scavengers cycle from the reduced form carrying the hydride anion with the high-energy electron back to the oxidized form lacking the hydride anion. Although there is a little loss, most of the free radical scavengers are rereduced and used over and over again.

This repeated use with only a little loss is why it ordinarily takes a small amount of these substances to do their electron carrying function to the maximum allowed by the availability of the hydride anion. The limiting factor in all this, in a well nourished person, is this rate-limited availability of the hydride anion with its high-energy electron.

The body can make NAD(P)H available for this purpose only at a limited rate. When the need to scavenge free radicals exceeds this rate, then symptoms, damage, and ageing occur. Adding more vitamins and other nutrients, even the ones noted as being free radical scavengers, notably vitamin C, vitamin E, vitamin A (especially á-carotene), cysteine, selenium, etc. do not, under ordinary circumstances, add much to all this.

All these free radical scavengers are cycled several times an hour when a person is sick. The NAD(P)H keeps rereducing these free radical scavengers so they are used repeatedly. Taking of the usual amounts of nutrient free radical scavengers only assures that there are no critical deficiencies that would limit this free radical scavenging electron-transfer chain described above. Still there is a normal limit to the free radical scavenging ability of this system…

ASCORBATE TO THE RESCUE

Except, ascorbate, C6H6O6H2, used as the source of electrons, not just as the electron carrier, can change all this. The C6H6O6H2 used in massive doses substitutes for the limited availability of the NAD(P)H. The C6H6O6 part of the C6H6O6H2 used this way is thrown away; the C6H6O6H2 is only used for the electrons it carries.

Amounts of 30 to 200+ grams of C6H6O6H2 provide ample high-energy electrons to directly scavenge the large amounts of free radicals generated in disease processes and provide enough high-energy electrons to rereduce NAD(P)+, FAD+, GSSG, tocopheryl quinone, etc. back to their reduced forms.

Lewin pointed out that although the C6H6O6H2/C6H6O6 redox couple is usually reduced by GSH at the concentrations in which these substances are ordinarily present, when C6H6O6H2 is present in large concentrations, it will reduce GSSG to GSH.

The usual direction of the redox reaction is reversed and the C6H6O6H2 supplies the high-energy electrons reducing the GSSG. If there was some substance that was cheaper, better tolerated by the body, and had fewer nuisance problems associated with its administration than sodium ascorbate, NaC6H6O6H, intravenously and intramuscularly, or ascorbic acid, C6H6O6H2, orally, I would use it.

So far, C6H6O6H2 and NaC6H6O6H are the premier sources of high-energy electrons and therefore the premier free radical scavengers. The dehydroascorbate, C6H6O6, part of the ascorbate, C6H6O6H2, used this way is excreted rapidly in the urine or metabolized further by the body. Although the complete pathway has not been described and involves some uncertainty, it is known that certain breakdown products of dehydroascorbate supply even more high-energy electrons.

Bearing in mind that it is the high-energy electron that is doing the free radical scavenging, one can see that animals which can synthesize ascorbate within themselves have a higher amount of the electron carrier available and will not ever suffer from scurvy. However, the high-energy electrons ultimately come from the same sources as in humans.

Ascorbate producing animals still must make the ascorbate and the high-energy electrons available by various metabolic steps using glucose. This process is rate- limited. Comparing the ability of a human to make C6H6O6H2 to a dog is like comparing a human’s ability to fly in a Concorde with a humming bird. The human can make enormous amounts of C6H6O6H2 in his chemical plants. Humans just have to learn to use it properly.

The usefulness of ascorbate in treating diseases involving free radicals bears no relationship to how much vitamin C animals make or consume unless one is satisfied with achieving only the level of health of that animal. We are using a natural substance in an unnatural way to achieve these effects. It is the high-energy electrons, not the ascorbate, that is most important here.

The mechanism I am describing is a pharmacologic effect of the high-energy electrons carried by the C6H6O6H2 that transcends the normal ability of any species of animal to ameliorate or conquer diseases involving free radicals. Any disease process that involves free radicals can be ameliorated by the high-energy electrons carried by ascorbate when used properly in massive doses.

It is true that there are certain logistic problems involved in delivering the massive doses of C6H6O6H2 containing the enormous numbers of electrons sufficient to quench the excessive free radicals of certain severely toxic diseases but it is surprising what massive doses of ascorbate will accomplish.

RAPID UTILIZATION OF THE HIGH-ENERGY ELECTRONS

Calculations of the total amount of ascorbate in a healthy person (pool size) with an intake of about 100 milligrams of vitamin C per day is roughly 2-3 grams and the turnover half time is about 20 days (28).

When a person who when well can ingest only 15 grams of ascorbic acid per 24 hours before it causes diarrhea, can take over 200 grams in 24 hours when ill with mononucleosis, one obtains a suggestion of the numbers of extra electrons involved. If 185 grams (200 minus 15) extra is used, whatever the amount of high-energy electrons carried in that divided by the amount in 3 grams means that if ascorbate was the only carrier of electrons (which it is not), that 3 grams of ascorbate would be rereduced about every 23 minutes.

There are so many facts such as the amount of high-energy electrons carried by the other free radical scavengers that this number is almost valueless. Still, it makes one think in terms of minutes to a few hours for the rereduction of all the free radical scavengers of the body when one is seriously ill. This emphasizes the futility of using vitamin free radical scavengers in the doses described in the RDA (29) to provide the necessary high-energy electrons.

A SIMPLE ANALOGY

Suppose you had a house out in the country that had a water well about 300 yards away. Between the house and the well are two high fences. Your house catches on fire and your neighbors come running with their buckets. One group sets up a bucket brigade between the well and the first fence and pours the water through a hole in the fence into the buckets of the second bucket brigade. The second bucket brigade runs to the second fence to pour the water through a hole in the second fence into the buckets of the third bucket brigade who throw the water on the fire.

Unfortunately, the fire goes out of control and it is not possible to pump the water out of the well at a rate fast enough to put out the fire. The arrival of more neighbors does no good because there are already enough for the three bucket brigades. A couple of neighbors run from their homes with their buckets full of water but that does not help very much. Then the fire engine roars up and puts out the fire with hoses that draw water from the fire engine. The firefighters do not rely on the water from the well. We have to stretch the analogy here a little but imagine microscopic buckets with C painted on their sides carrying the water out of the fire hose. The little buckets are wasted. Their only function is to carry the water.

CONCLUSION

Free radical scavenging is a very dynamic process. The nutritional free radical scavengers in the diet, including vitamin C, are not for the purpose of providing the large number of high- energy electrons necessary to meet the rate with which free radicals are made. The purpose of dietary free radical scavengers is to replace those scavengers incidentally lost. The process of reducing a free radical does not destroy a free radical scavenger if it is rereduced before being further broken down. The free radical scavengers are intermediaries.

It is up to other metabolic processes to provide the high-energy electrons with which the free radical scavengers reduce free radicals. The rate at which free radicals are formed becomes excessive and causes symptoms when it exceeds the rate of reduction of those free radicals. Part of the reduction is spontaneous and part is enzymatic. The remainder must be reduced by the high-energy electrons carried by the nonenzymatic free radical scavengers.

Ascorbate in massive doses can perform an unusual function. When doses of 30 to 200+ grams per 24 hours are used, the high- energy electrons carried in on the administered ascorbate adds significantly and decisively to the actual electrons doing the reducing. The ascorbate is not used as the vitamin C where it is rereduced by NAD(P)H and used repeatedly; it is used for the high- energy electrons it carries.

In high concentrations ascorbate reduces NAD(P)H and provides the high-energy electrons necessary to reduce molecular oxygen used in the respiratory burst of phagocytes. In these functions, the ascorbate part is mostly wasted but the necessary high-energy electrons are provided in large amounts.

The opportunity to reduce the human suffering from the free radicals of infectious diseases, autoimmune diseases, allergies, trauma, burns, surgery, toxins, and to a degree ageing, etc., which could be neutralized by high-energy electrons carried by high doses of C6H6O6H2 is immense.

Thursday, 20 February 2025

The Case Against Fluoride

The Case Against Fluoride: How Hazardous Waste Ended Up in Our Drinking Water and the Bad Science and Powerful Politics that Keep it There

By Paul Connett, PhD, James Beck, MD, PhD, & H.S. Micklem, DPhil
Chelsea Green Publishing, 2010


On the label of every tube of fluoride toothpaste is a statement which reads, “Drug Facts: Active Ingredient—Sodium Fluoride … Keep out of reach of children under six years of age. If more than used for brushing is accidentally swallowed, get medical help or contact a Poison Control Center right away.” The amount recommended for brushing is about the size of a pea. This pea-sized dab contains about the same amount of fluoride as one glass of water in areas that fluoridate the water. Do you drink the recommended eight glasses of water per day? Do you call the Poison Control Center when you do?

The insanity of intentional water fluoridation is examined from every angle in this book. International law forbids dumping fluoride waste into the sea but it is accepted in American drinking water. As stated in the toothpaste disclaimer above, the FDA officially considers fluoride to be a drug. This drug has never been approved by the FDA. Contaminating drinking water with fluoride can be most charitably characterized as an experiment which violates the Nuremburg Code prohibiting experimental human treatment without informed consent. China, India, Japan and most of Europe do not fluoridate their water.


 One of the first studies claiming the safety of fluoride was done by Cox and Hodge. Cox worked for the giant aluminum company Alcoa. At that time fluoride was a major waste product of aluminum processing. It must have seemed like a wondrous miracle when Cox discovered that this toxic waste was safe and effective for preventing tooth decay when added to the water supply. The real miracle is that so many people apparently believe this. Hodge worked on the Manhattan Project supervising experiments on unsuspecting patients who were injected with uranium and plutonium. These guys have all the credibility of those famous leading scholars named Larry, Curly and Moe. If you believe the studies and health advice of Cox and Hodge, you might want to consider cutting back on eating those old lead-based paint chips.

Many other studies are reviewed, such as those of Dr. Phyllis Mullenix, who not only had no conflict of interest with the commercial entities involved but in fact suffered professionally for daring to suggest that fluoride might be problematic.

John Colquhoun of New Zealand promoted fluoride enthusiastically around the country for years. After traveling the world to survey the effects of fluoride, he realized he was quite wrong. Colquhoun was a man of rare courage and integrity, and spent the rest of his life trying to undo the damage he had done.


 When the National Research Council came out with a report—over five hundred pages long—unfavorable to fluoride, the American Dental Association took less than one day to dismiss it. The Centers for Disease Control rejected it six days later. The director of Quackwatch called fluoride opponents “poison-mongers.” The irony piles pretty high when you consider that most opponents are unpaid and do much of this on their own dime, they have nothing to monger or sell, and are trying to remove the poison, not add it.

Toward the end of the book the authors pull out one of my all-time favorite quotes from the late Michael Crichton. “Historically, the claim of consensus has been the first refuge of scoundrels; it is a way to avoid debate by claiming that the matter is already settled….The greatest scientists in history are great precisely because they broke with the consensus. . . There is no such thing as consensus science. If it’s consensus, it isn’t science. If it’s science, it isn’t consensus.


This article appeared in Wise Traditions in Food, Farming and the Healing Arts, the quarterly magazine of the Weston A. Price Foundation, Spring 2011.






Monday, 17 February 2025

Fluoridation rests upon a blatant lie

In 2014 the Chief Science Advisor and the NZ Royal Society produced a Report on fluoridation. The conclusion on fluoride and IQ contains a blatant lie.

The Report claims the loss of 7 IQ points (described as “less than one standard deviation”) found in a 2012 Harvard review of human fluoride-IQ studies “is likely to be a measurement or statistical artefact of no functional significance.” This conclusion is a blatant lie. If the truthful conclusion had been reported, it would have said “is likely to be a measurement OF functional significance”, the whole trajectory of fluoridation in New Zealand would have been entirely different.


Everyone in New Zealand should be aware of this deception.


Watch video at 11 minutes in to see visual presentation of this lie. https://www.youtube.com/watch?v=k5WwNKP0WRI&t=655s

 

Thursday, 13 February 2025

Water Fluoridation by Paul Connett

The Latest Science Indicates That the Practice Must Stop

Water fluoridation is the deliberate addition of a substance containing, or yielding, fluoride (that is, in the form of the free fluoride ion) to the public water supply with the ostensible aim of reducing tooth decay. The concentrations of fluoride used for this purpose in the U.S. range from 0.7 to 1.2 milligrams of fluoride per liter of water (0.7-1.2 parts per million or ppm). When the practice began in the U.S. and Canada in 1945 there were no published studies available which demonstrated that consuming fluoride at these levels was safe.

Without any formal study, it was assumed that because some people in some places had consumed natural fluoride levels higher than 1 ppm for many years, with no “apparent” harm recorded, adding fluoride to water would be safe.

The authors both work for the Fluoride Action Network (FAN),1 a nonprofit dedicated to education and sharing information on the toxicity of fluoride. FAN maintains the largest database dedicated to fluoride’s toxicity on blood,2 bone,3 brain,4 heart,5 kidney,6 liver,7 lung,8 the reproductive system,9 and the thyroid gland;10 as well as the largest collection of news articles on fluoride11 that are accessible by country, by state for the U.S. and by province for Canada. The website also contains links to many videotaped interviews,12 government reports by country,13 fluoride industrial emissions by state14 and more.

NEITHER ETHICAL NOR SCIENTIFIC

It was neither ethical nor scientific to force people to consume fluoride in 1945, and it is not ethical or scientific to do it today. The arguments get stronger as U.S. authorities are finally getting around to doing the studies on tissues that they should have conducted many years ago—and should have done before they started what has amounted to one of the largest public health experiments in U.S. history.

PROTECTING A BELIEF SYSTEM

The dilemma for those who believe that this practice is causing harm is how to end it when most people don’t even know their water is being fluoridated and don’t know the potential risks it may be posing to their children. Sadly, most doctors and dentists simply follow the policies of their professional bodies without reading the literature for themselves. The media are not telling the public about the latest health studies and are simply parroting statements from organizations like the American Dental Association (ADA) and agencies like the Oral Health Division of the Centers for Disease Control and Prevention (CDC), which hold a long standing “belief” in the “safety and effectiveness” of this practice. Meanwhile, government health departments at all levels appear to be more interested in protecting this outdated policy than protecting the health of our children.

The task that FAN has set itself since 2000 is to share the science about the dangers posed by this practice with those who are willing to read and listen, mainly through our web page at FluorideALERT.org and through public presentations (for example, in Seattle15). The latest science makes it very clear that the practice of fluoridation must stop!

FLUORIDE AND INTELLIGENCE

In 2006, the National Research Council (NRC) of the National Academies concluded that “fluorides have the ability to interfere with functions of the brain”16 and for the first time called fluoride an endocrine disruptor.17

In 2006, there were only five IQ studies available to the NRC panel. Subsequently, many more have been published (including studies that were previously only available in Chinese). As of 2019, we now have sixty studies, fifty-three of which have shown a lowered IQ in children in communities with high fluoride exposure compared to communities with lower fluoride exposure.18

Most of these studies have been carried out in China, but others took place in India, Iran and Mexico. In 2012, twenty-seven of these studies were subjected to a meta-analysis by a team from Harvard, which was published in one of the world’s leading environmental health journals, Environmental Health Perspectives.19 While this team had concerns about the lack of information on several possible confounding factors in many of these studies, they were struck by the consistency of the results. Even though the research was carried out over a period of twenty-one years, by many different research teams, in two countries (China and Iran) and in many different locations, twenty-six out of the twenty-seven studies found the same result: a lowering of IQ. The average lowering was seven IQ points.

It should be noted that a shift downward of five IQ points in a large population would halve the number of very bright children (IQ greater than one hundred thirty) and increase by over 50 percent the number of mentally handicapped (IQ lower than seventy). Such a downward shift would have both huge economic and social consequences for a country like the USA.

Promoters of fluoridation have done their best to diminish the significance of these findings for fluoridated communities, but recent findings have largely undermined their self-serving arguments. A rigorous U.S. government-funded study carried out by a highly qualified research team headed by Dr. Morteza Bashash confirmed that fluoride is neurotoxic at levels currently experienced in fluoridated communities and, for this effect, the most vulnerable stage of human life is during fetal development.20 This study was conducted in Mexico City with two hundred ninety-nine mother-offspring pairs. The authors found strong associations between fluoride exposure to the pregnant women (as measured in their urine) and lowered IQ in their offspring at age four and again at six to twelve years of age. Subsequently, in 2018, a study reported that the lowering of IQ in the same cohort also occurred in an earlier age range (one to three years).21

In 2018, using the same Mexico City cohort, Dr. Bashash found that there was a strong association between some of the symptoms of ADHD in the children and urine fluoride levels in the pregnant women.22 A 2015 study found a relationship between the prevalence of ADHD in the U.S. and fluoridation status by state; the higher the percentage of the state fluoridated, the greater the prevalence of ADHD.23

It is hard to overstate the importance of the 2017 Bashash study.20 Strikingly, it was funded by U.S. government agencies, two of which (National Institutes of Health and the Environmental Protection Agency) have promoted (NIH) and defended (EPA) the safety of water fluoridation. The study was part of a twenty-five-year ELEMENT research project (Early Life Exposures in Mexico to Environmental Toxicants) directed by professor Howard Hu from the University of Toronto. The Bashash study took over twelve years and involved researchers from many distinguished universities and institutions in Canada, the U.S. and Mexico. These included the universities of Toronto, McGill, Indiana, Illinois, Michigan, Harvard, as well as Mount Sinai and the National Institute of Perinatology in Mexico. These researchers have published over fifty studies conducted along similar lines for other neurotoxicants. Of particular importance was the fact that, unlike most of the other IQ studies on fluoride, this study involved measurements at the individual (not community) level for both mother and child. Based upon their extensive experience, the authors controlled for a large number of potential confounding variables, and even after controlling for these they still found a very strong relationship between fluoride exposure during pregnancy in the mother and lowered IQ in their offspring.

Fluoridation promoters, including the American Dental Association, have claimed that this study was not relevant to fluoridated communities in the U.S. because Mexico City does not have artificial fluoridation and pregnant women there are likely to have higher doses of fluoride from fluoridated salt and some naturally fluoridated water areas. Such arguments are not convincing because the biometric of exposure used was fluoride levels in the urine, which is a measure of total dose of fluoride and is independent of the source. Moreover, the range of exposure in Mexico City was within the range of fluoride levels in the urine of adults in the U.S. This point was further confirmed by a subsequent national study of the urine fluoride levels in pregnant women in Canada. This study found that levels of fluoride in the urine of Canadian women living in fluoridated communities were almost identical to the levels in Mexico City, namely 0.87 ppm in Canada versus 0.91 ppm in Mexico City.24

As far as the politics of fluoridation are concerned, it is significant that some of the world’s leading neurotoxicologists, like Phillipe Grandjean (mercury specialist) and David Bellinger (lead specialist), are now participating in this research as well as reviewing the literature.25,26 They now see fluoride’s neurotoxicity in the same vein as that of lead, arsenic, mercury and other well-established neurotoxicants.

It should also be stressed that in addition to the fifty-three IQ studies discussed above, there are many other animal, human, biochemical and cellular studies that provide an overwhelming weight of evidence that fluoride is neurotoxic. These include one hundred thirty human brain studies;27 two hundred forty-one animal brain studies;28 thirty-three cellular brain studies;29 and thirty review studies.30

FLUORIDE AND HYPOTHYROIDISM

In the 1930s, ’40s and ’50s, doctors in Argentina, France and Germany used sodium fluoride to lower the activity of the thyroid gland for those suffering from hyperthyroidism (overactive thyroid gland).31 -37 Despite this knowledge, government agencies in the U.S. and other fluoridating countries have never seen fit to investigate a possible relationship between fluoride exposure and the rising level of hypothyroidism in their countries. Only recently have scientists reviewed the matter.38-41

A 2018 study, reported that while they could find no relationship between fluoride exposure and TSH levels (thyroid stimulating hormone and an indicator of hypothyroidism) and fluoridation status among the general population, they did find that for those who had low or even borderline iodine intake, fluoride exposure was associated with an increase in their TSH levels.42 

The importance of this finding is that it gives a very plausible mechanism for why fluoride might lower IQ in children born to mothers with high fluoride exposure. When the fetus comes into existence it has no thyroid gland. It is entirely dependent on the mother’s thyroid levels for its early mental development. So any depression in the mother’s thyroid hormone levels will increase the risk of lowered IQ in their offspring (see Vyvyan Howard’s explanation of this situation in a PowerPoint presentation he gave in New Zealand in 2018).43

WARNING PREGNANT WOMEN

One of the sad consequences of the medical community’s acceptance of the safety-and-effectiveness argument for water fluoridation, based upon dogma rather than upon the latest science, is that many doctors are oblivious of these findings. The result is that women are not being warned to avoid fluoride exposure during pregnancy. They are not being warned by their doctors, by health departments, by professional bodies or by the media. It has been left to non-governmental bodies like FAN to get the word out the best we can via social media, the Internet (see the Moms 2B Campaign),44 press releases,45 leaflets and talks. We have been trying to do so since 2017, but it is an extremely difficult task, as is the continuing battle to try to end the well-entrenched practice of water fluoridation.

LAWSUIT PROVIDES NEW HOPE

In November 2016, the Fluoride Action Network, along with Food & Water Watch, the American Academy of Environmental Medicine, the International Academy of Oral Medicine and Toxicology, Moms Against Fluoridation, the Organic Consumers Association and individuals, petitioned the EPA46 to ban the deliberate addition of fluoride to public drinking water under provisions in the Toxic Substances and Control Act.

We argued that “[t]he risk to the brain posed by fluoridation additives is an unreasonable risk because, inter alia, it is now understood that fluoride’s predominant effect on tooth decay comes from topical contact with teeth, not ingestion. Since there is little benefit in swallowing fluoride, there is little justification in exposing the public to any risk of fluoride neurotoxicity, particularly via a source as essential to human sustenance as the public drinking water and the many processed foods and beverages made therefrom. The addition of fluoridation chemicals to water thus represents the very type of unreasonable risk that EPA is duly authorized to prohibit pursuant to its powers and responsibilities under Section 6 of TSCA, and Petitioners urge the Agency to exercise its authority to do so.”

In September 201747 the EPA rejected our petition on its scientific merits. In response to an appeal from FAN, a federal court denied EPA’s motion to dismiss in December 2017.48

Also in December 201749 the EPA argued that no other studies should be added to the case after our petition was first delivered to them in November 2016. The court disagreed with EPA50 and ruled to allow new studies, such as those by Bashash and others discussed above. A trial date has been set to take place in federal district court in San Francisco in August 2019.

We are confident that we can win this case. In order to do so, it will require us to demonstrate three things: 1) that fluoride poses a hazard to the developing brain; 2) that there is a risk at current exposure levels (from all sources combined) in fluoridated communities; 3) that this is an unreasonable risk because there are other ways that tooth decay can be prevented.

Moreover, even if fluoride is one of those alternatives, there are other and more appropriate ways of delivering fluoride to the surface of teeth than putting fluoride into the drinking water. Indeed, the majority of countries worldwide that do not fluoridate their water have actually demonstrated this over many years.

SUMMARY AND CONCLUSIONS

There are many ethical and scientific arguments against the seventy-year practice of water fluoridation. The evidence that swallowing fluoride reduces tooth decay remains weak. Not a single randomized controlled trial has been attempted to demonstrate this, and promoters have relied on studies with far weaker methodologies.65 Meanwhile, the number of studies that indicate harm can be caused, even at the doses experienced in fluoridated communities, has been growing, particularly studies on the brain.20,22,24,42,46 

With such risks on the table, it is unconscionable, in our view, that governments continue to promote the deliberate addition of a known neurotoxic and endocrine-disrupting substance to the drinking water of millions of people, most of whom have not been informed of the risks involved, or been given the opportunity to give—or refuse—their consent on the matter.


SIDEBARS

ELEVEN ARGUMENTS WHY FLUORIDATION SHOULD BE ENDED
1. Fluoridation is unethical. Using the public water supply to deliver dental therapy goes against all recognized principles of modern pharmacology and ethical healthcare practice. It imposes medication on all water consumers indiscriminately and without the individual’s informed consent. These include the unborn, bottle-fed infants, persons with chronic diseases known to be aggravated by fluoride (such as poor kidney function), the poorly nourished (such as those with low iodine intake) and the elderly. It does so with uncontrolled dosage, no monitoring of adverse effects and no possibility of avoiding treatment for most, if not all, people. This is especially true for those on a low-income budget who simply cannot afford avoidance measures like reverse osmosis filtration systems.
2. Fluoridation is unusual. The vast majority of countries worldwide do not fluoridate their drinking water. Out of one hundred ninety-six countries, only twenty-four have any fluoridated cities, and of those, only ten, including the U.S., fluoridate more than half their population. Ninety-five percent of the world’s people drink water without artificial fluoridation. Over half of those who do, live in the U.S. In Europe, where forty-three out of forty-eight nations have no water fluoridation, 98 percent of the population is not forced to drink fluoridated water. A few European countries (namely France, Germany, Switzerland and Austria) have fluoridated salt available, but people are not forced to buy this salt, as non-fluoridated salt is also available. Despite this, World Health Organization (WHO) data61 indicate that since the 1960s, tooth decay in twelve-year-olds has been coming down as fast in non-fluoridated countries as in fluoridated ones.
3. Children in fluoridated communities are being grossly over-exposed to fluoride. In the U.S. and other fluoridated countries, there has been a dramatic increase in young children and teens in the prevalence of dental fluorosis (discoloration of tooth enamel caused by low-level systemic fluoride toxicity during tooth formation). This condition indicates that children have been grossly over-exposed to fluoride before their permanent teeth have erupted. The latest national survey indicates that over 60 percent of U.S. teens have dental fluorosis.52,53 Of those, 24 percent have moderate and nearly 2 percent have severe levels of the disease. These levels can produce yellow and brown staining and structural damage to the enamel. To put this into context, the early promoters of fluoridation anticipated only 10 percent of the children in fluoridated communities would be affected by this condition, and these would be only in the “very mild” category. They believed that this was an acceptable trade-off for reducing tooth decay. Even avid promoters of fluoridation no longer accept that the current prevalence rates as acceptable but they tend to blame other sources of fluoride—rather than water fluoridation—for the dramatic increase. In reality, every source of fluoride ingested contributes to this prevalence. The contribution from water fluoridation can be eliminated with a simple policy change.
4. Fluoride has the potential to damage many other tissues. Because of the prevalence of dental fluorosis, there is no question that fluoride can damage the developing teeth. Nor is there any question from the evidence provided in countries with large areas of endemic fluorosis (such as India and China) where millions of people have both dental and skeletal fluorosis, that high doses of fluoride can damage other tissues including bones, connective tissue, the brain, the endocrine system, the gut and kidneys. The Indian Ministry of Health & Family Welfare,54 provides an excellent description of the problems faced by thousands of villages poisoned by fluoride. For the Western world, much of this evidence was provided in a comprehensive review of the literature conducted by the National Research Council of the National Academies in 2006.16 What has emerged since 2006 is a growing body of evidence that this harm can occur at doses experienced in artificially fluoridated  communities.
5. Fluoridation is unnecessary. Fluoride is not an essential nutrient. No one has ever demonstrated that a single biological process in the human body needs fluoride to function properly. There is no such thing as a “fluoridedeficiency” disease. Children can have perfectly good teeth without ingesting fluoride. Even promoters of water fluoridation admit that the predominant benefit of fluoride is topical, not systemic.55-58 Thus, it is morally indefensible to force people to ingest fluoride via the public water supply, when for those who want fluoride,  fluoridated toothpaste is universally available. Moreover, the fluoride used in toothpaste is pharmaceutical grade whereas the fluoride used to fluoridate water is an industrial grade hazardous waste product from the phosphate fertilizer industry.25
6. Today’s fluoride is worse. The fluoridating chemical used in over 90 percent of the fluoridating communities in the U.S. is a substance called hexafluorosilicic acid (H2SiF6). This substance is removed from the scrubbing systems of the phosphate fertilizer industry as a 23-25 percent solution. It is contaminated with trace amounts of other toxic substances including aluminum, arsenic, lead and radioactive isotopes (the same ore that is mined for fluoride in Florida is also mined for uranium). Ironically, this waste product cannot be dumped into the sea by international law, but health authorities blandly allow it to be put untreated into the public water supply!
7. Fluoride is very toxic and nature has developed protection mechanisms for many living things. For lower creatures like bacteria and fungi, there are genes—switched on by high levels of fluoride—which code for proteins called fluoride exporting proteins (FEX proteins). These proteins are located in the cellular membranes and pump fluoride out of the cell.26 In mammals, the kidney excretes about 50 percent of fluoride ingested each day from healthy individuals, and most of the rest is rapidly sequestered in hard tissues like the bones. Importantly, the human breast appears to act as a fluoride filter for the new born baby. The level in mothers’ milk is remarkably low (0.004 ppm).27 Thus, a bottle-fed baby, when the formula is made up with fluoridated tap water (0.7 to 1.2 ppm), will get approximately two hundred times more fluoride than a breastfed infant (that is, two hundred times more than nature intended).
8. Fluoridation is unscientific. Fluoridation is promoted with PR techniques like endorsements, not with sound
science. Most of the endorsements were made shortly after the U.S. Public Health Service endorsed water fluoridation in 1950 with virtually no science on the short-term—let alone long-term—health effects. Citizens should be very wary of taking such endorsements at face value unless they are accompanied by an up-to-date review of the literature—and very few are. Incredibly, in over seventy years there has been no randomized control trial (RCT) to demonstrate that swallowing fluoride lowers tooth decay. As far as the U.S. Food and Drug Administration (FDA) is concerned, an RCT is the gold standard for approving new drugs. According to the FDA, fluoride is an unapproved drug28 and the FDA has never approved fluoride tablets for ingestion. Many decision makers and journalists around the world are impressed when they read the notorious statement from the CDC in 1999 that “Fluoridation is one of the top public health achievements of the 20th century.”63 However, what they may not realize is that this statement did not come from the CDC itself (which has about thirty thousand employees, many of whom are highly qualified in many medical fields as well as toxicology) but from the CDC’s small Oral Health Division with only thirty employees, most of whom only have dental qualifications. Moreover, their job is defined as promoting fluoridation. They even admit to not following—or being responsible for—the science pertaining to fluoride’s harmful effects. Journalists and others have been impressed by a public relations exercise by a promotional body, not by a body that maintains a careful overview of any harm the practice may be causing.
9. Health risks are ignored in fluoridated countries. Sadly, because the imposed dental practice of water fluoridation is so entrenched in the psyche of the medical, dental and public health establishments in fluoridated countries, neither governments nor the mainstream media are warning the public about the large and growing
body of scientific research30 that shows that fluoride exposure poses many health risks.
10. Fluoridation violates the precautionary principle. The scientific evidence that swallowing fluoride lowers tooth decay is weak,31 but the weight of evidence that it causes harm to the developing brain is so one-sided, that to wait for further studies before halting the deliberate addition of fluoride to water is a rash and irresponsible public health position.
11. Fluoridation violates the principles of environmental justice. The addition of fluoride to public water is an environmental injustice to people living in poverty in fluoridated areas who do not have access to alternative water
sources and are captive to tap water for all their water needs. Moreover, it is well established that those with poor
nutrition are more vulnerable to fluoride’s toxic effects, and poor nutrition is more likely to occur among those
with low incomes.


REFERENCES
1. Fluoride Action Network, website http://fluoridealert.org/.
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37. Galletti and Joyet. 1958. Effect of fluorine on thyroidal iodine metabolism in hyperthyroidism. The Journal of Clinical Endocrinology and Metabolism. Oct;18(10):1102-10. http://fluoridealert.org/wp-content/uploads/galletti-1958.pdf
38. Peckham et al. 2015. Are fluoride levels in drinking water associated with hypothyroidism prevalence in England? A large observational study of GP practice data and fluoride levels in drinking water. Journal of Epidemiology and Community Health. Jul;69(7):619-24. http://fluoridealert.org/wp-content/uploads/peckham-2015.pdf
39. Chaitanya et al. 2018. A systematic analysis on possibility of water fluoridation causing hypothyroidism. Indian Journal of Dental Research. May-Jun; 29(3):358-363. http://fluoridealert.org/studytracker/31383/
40. McLaren JR. 1969. Fluoride and the thyroid gland. Editorial. Fluoride. Oct; 2(4):192-194. http://fluoridealert.org/wp-content/uploads/mclaren-1969.pdf.
41. Gas’kov et al. 2005. The specific features of the development of iodine deficiencies in children living under environmental pollution with fluorine compounds. Gigiena i Sanitariia. Nov-Dec;(6):53-5. http://fluoridealert.org/studytracker/15213/.
42. Malin et al. 2018. Fluoride exposure and thyroid function among adults living in Canada: Effect modification by iodine status. Environment International. 121:667-674. http://fluoridealert.org/wp-content/uploads/malin-2018.pdf.
43. Vyvyan Howard, FRCPath, http://fluoridealert.org/howard-2018-nz/.
44. Moms2B Campaign, http://fluoridealert.org/issues/moms2b/.
45. Fluoride Action Network , Press Releases, http://fluoridealert.org/news/?country=united-states&sub=fluoride-action-network-press-release-unitedstates.
46. Connett M. 2016. Petition to the U.S. Environmental Protection Agency under Section 21 of the Toxic Substances Control Act (TSCA), 15 U.S.C. § 2620, invoking Section 6 of TSCA, 15 U.S.C. § 2605(a), on behalf of several groups and individuals. November 22. http://fluoridealert.org/wp-content/uploads/epa-petition.pdf.
47. U.S. EPA (Environmental Protection Agency). 2017. Federal defendants’ motion to dismiss. In the United States District Court for Northern California, San Francisco Division. Case 3:17-cv-02162-EMC, Document 28. September 25. http://fluoridealert.org/wp-content/uploads/tsca.epa-motion-to-dismiss.9-25-17.pdf.
48. United States District Court for Northern California. 2017. Order denying defendant’s motion to dismiss. Case No. 17-cv-02162-EMC, Docket No.28. December 21. http://fluoridealert.org/wp-content/uploads/tsca.12-21-17.denies-epa-motion-to-dismiss.pdf.
49. U.S. EPA (Environmental Protection Agency). 2017. Federal defendants’ notice of motion and motion to limit review to the administrative record and to strike plaintiffs’ jury demand. Case No.: 17-cv-02162-EMC. December 14. http://fluoridealert.org/wp-content/uploads/tsca.12-14-17.epa-requests-protective-order-to-limit-discovery.
pdf.
50. United States District Court for Northern California. 2018. Order Denying Defendant’s Motion to Limit Review to the Administrative Record. Case 3:17-cv-02162-EMC, Document 53, February 7. http://fluoridealert.org/wp-content/uploads/tsca.2-7-18.court-denies-epa-motion-to-limit.pdf.
51. WHO Data, http://fluoridealert.org/issues/caries/who-data/.
52. Wiener et al. 2018. Dental fluorosis over time: a comparison of national health and nutrition examination survey data from 2001-2002 and 2011-2012. Journal of Dental Hygiene. Feb;92(1):23-29.
53. Neurath et al. 2019. Dental fluorosis trends in United States oral health surveys: 1986-2012. Journal of Dental Research Clinical & Translational Research. In print.
54. Ministry of Health & Family Welfare, National Health Portal of India. 2016. Fluorosis. http://fluoridealert.org/studytracker/33368/.
55. Centers for Disease Control & Prevention. 1999. Achievements in public health, 1900-1999: fluoridation of drinking water to prevent dental caries. Morbidity and Mortality Weekly. October 22, 1999 /48(41);933-940. http://fluoridealert.org/wp-content/uploads/cdc-mmwr.oct-22-1999.pdf.
56. Centers for Disease Control & Prevention. 2001. Recommendations for using fluoride to prevent and control dental caries in the United States. Morbidity and Mortality Weekly Review. Recommendations and Reports, August 17, 2001 / 50(RR14);1-42.
57. Ibid at 16.
58. Featherstone JD. 2000. The science and practice of caries prevention. Journal of the American Dental Association. July: 131(7):887-99.
59. Fluoride Action Network, Phosphate Fertilizer Industry, see http://fluoridealert.org/articles/phosphate01/
60. Li et al. 2013. Eukaryotic resistance to fluoride toxicity mediated by a widespread family of fluoride export proteins. Proceedings of the National Academy of Sciences of the United States of America. Nov 19;110(47):19018-23.
61. Ibid at 16, page 40, https://www.nap.edu/read/11571/chapter/4#40.
62. Moore, Robert J. 2005. Fluoride is an unapproved drug. Letter from Food and Drug Administration to Daniel Stockin. www.fluoridealert.org/wp-content/uploads/fda-2005a.pdf.
63. Centers for Disease Control & Prevention. 1999. Ten Great Public Health Achievements–United States, 1900-1999. Morbidity and Mortality Weekly Review. December 24, 1999 / 48(50);1141
64. Fluoride Action Network. Study fluoridealert.org/studytracker/.
65. Iheozor-Ejiofor Z, et al. 2015. Water fluoridation for the prevention of dental caries. Cochrane Database of Systematic Reviews. June 18. https://www.cochranelibrary.com/cdsr/doi/10.1002/14651858.CD010856.pub2/abstract.

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