DENTAL FLUOROSIS IN GOZO · DENTAL FLUOROSIS IN GOZO A Dissertation Submitted in Part-FulfIlment of...

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DENTAL FLUOROSIS IN GOZO A Dissertation Submitted in Part- FulfIlment of the Requirements for the Degree of Masters of Science in Public Health Medicine of the University of Malta Ethel Vento Zahra August 2007

Transcript of DENTAL FLUOROSIS IN GOZO · DENTAL FLUOROSIS IN GOZO A Dissertation Submitted in Part-FulfIlment of...

Page 1: DENTAL FLUOROSIS IN GOZO · DENTAL FLUOROSIS IN GOZO A Dissertation Submitted in Part-FulfIlment of the Requirements for the Degree of Masters of Science in Public Health Medicine

DENTAL FLUOROSIS IN GOZO

A Dissertation Submitted in Part- FulfIlment of the Requirements for the Degree of Masters of Science in

Public Health Medicine of the University of Malta

Ethel Vento Zahra

August 2007

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Declarations

I, the undersigned, declare that this dissertation is my original work, carried out under the

supervision of Dr Pauline J. Vassallo BChD, MSc (Lond.), DDPH, RCS (Eng.), MBA

(Warwick), Consultant in Dental Public Health.

Ethel Vento Zahra

I, the undersigned, declare that in my opinion this dissertation is good enough to warrant

at least a pass by the MSc Public Health Examination Board.

Pauline Vassallo

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Dedication

To my family and friends. Thanks for all the love and support.

You're all special and irreplaceable!

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The successful completion of this dissertation would not have been possible

without the encouragement and help of several people.

I would like to express my sincere gratitude to my supervisor Dr Pauline J.

Vassallo B.Ch.D, MSc (Lond.), DDPH, RCS (Eng.), MBA (Warwick), Consultant

in Dental Public Health, for her patience, support and guidance with this project.

I would also like to thank Dr Neville Calleja MD, MSc, MSc (Lond), DLSHTM

Grad. Stat., Principal Medical Officer in Medical Statistics within the Department

of Health Information, for his immense patience and assistance in the statistical

analysis of the study results.

I am immensely grateful for the assistance given to me by the dental hygienists at

Gozo General Hospital, in particular Mr. Paul De Brincat and Mr. Martin Vella

who acted as my guides and scribes. Without them I would probably still be lost in

Gozo, vainly trying to fmd the next school on my list.

My fmal thanks go to all my family and friends who, in their own various ways,

have been supporting me patiently throughout this course of study.

Ethel Vento Zahra University of Malta

August 2007

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SUMMARY

The aim of this study was to examine the levels of dental fluorosis in 5 year old and 12 year

old school children, so as to evaluate if dental fluorosis in Gozo is presently a public health

problem. A path finder survey carried out in 1986 by Moller suggested that dental fluorosis

was a public health problem since values of >0.6 using Dean's index were recorded.

These exceeded the threshold value of 0.4-0.6. However, Moller himself questioned the

results due to the possibility that other enamel opacities were included as dental fluorosis.

The objectives of this study were:

1. To determine prevalence of fluorosis in the deciduous dentition in Gozo, which

has never been determined previously.

2. To establish how large a public health problem dental fluorosis currently is in

both the deciduous (in 5 year oIds) and the permanent dentition (in 12 year olds)

in Gozo.

3. To determine how aware the 12 year old Gozitan children are about the aesthetic

changes to their upper central incisors, associated with dental fluorosis.

4. To serve as a comparison for future studies which may be carried out to determine

the effect of polished water on fluorosis prevalence in the same population.

All 5 year old and 12 year old children with a signed consent form, present at the school on

the day of the visit were examined clinically, and observations were recorded using the TF

Index. Intraexaminer reliability was tested. Locality of residence in the case of 5 year olds

and locality of residence up to 6 years of age in the case of the 12 year old children was

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recorded. The 12 year old children were also asked a question to detennine awareness of

aesthetic changes associated with dental fluorosis. The data collected was analysed using the

SPSS software package.

The results show negligible dental fluorosis in the 5 year old age group. 13.8 % of the 12

year olds had marks attributable to dental fluorosis on their upper anterior teeth, out of

which only 4% have mild to moderate fluorosis (fF scores 3 to 5), the worst result recorded.

Only 0.86 % of all the 12 year old children examined were aware of marks attributable to

fluorosis on their upper anterior teeth.

The difference in fluorosis between localities is statistically significant (p = 0.(05). No

correlation (p = 0.68) was found between mean fluoride concentrations (1994 to 2000) for

individual localities and mean dental fluorosis levels reported in the respective localities.

The conclusions drawn from this study are that:

• Dental fluorosis prevalence in Gozo is currently: negligible in the deciduous

dentition; low and mild in the permanent dentition. Therefore dental fluorosis in

Gozo is currently not a public health problem.

• The 12 year old children are not aware of the aesthetic changes associated with

dental fluorosis.

• There is a significant difference in the prevalence of dental fluorosis in the

permanent dentition when analysed by locality.

• The systemic source of dental fluorosis which is present in Gozo is not singularly

tap water, as was previously assumed.

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Contents

Table of Contents ................................................................................... i List of Tables ........................................................................................ iv List of Figures ....................................................................................... iv

Chapter 1

1.1 1.1.1 1.1.2 1.1.3 1.1.4 1.1.4.1 1.1.4.2 1.1.4.3 1.1.4.4 1.1.4.5 1.1.4.6 1.2 1.3 1.3.1 1.3.2

Chapter 2

2.1 2.11 2.2 2.2.1 2.2.2 2.2.3 2.3 2.4 2.5 2.5.1 2.5.2 2.6 2.6.1 2.6.2 2.6.3 2.6.4

Introduction ........... , ........................................................... 7

Background Infonnation: Gozo General Country Infonnation Politics Education Health Care System in Gozo Overview Dental Care System Human Resources Financing General Health Oral Health Water Supplies Aims and Objectives Aim Objectives

Literature Review .............................................................. 20

Introduction Fluorides in the Environment The Chemistry of Fluoride in Water Fluoride Vehicles Population Measures Individual Measures Professionally Applied Measures Fluoride Usage Fluoride as a Caries Preventive Agent Effect of Fluoride - Mechanism of Action Pre- Eruptive Effect Post- Eruptive Effect Fluoride and the Body Fluoride Intake by Man Absorption, Retention and Excretion Fluoride in Teeth and Bone Excretion

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2.7 2.7.1 2.7.2 2.S 2.S.1 2.S.1.1 2.S.1.2 2.S.1.3 2.S.1.4 2.S.2 2.S.3 2.9

Chapter 3

3.1 3.2 3.3 3.4 3.5 3.5.1 3.5.2 3.5.3 3.5.4 3.6

Chapter 4

4.1 4.1.1 4.1.2 4.1.3 4.2 4.3

Chapter 5

5.1

Fluoride Toxicity Acute Toxicity Chronic Toxicity Fluorosis Dental Fluorosis Indices of Dental Fluorosis Aesthetic Perceptions of Fluorosis Treatment Options for Dental Fluorosis Evidence of Dental Fluorosis in Gozo so Far Skeletal Fluorosis Other Effects Conclusion

Methodology ...................................................................... 59

General Design of the Study Literature Review Examiner Training Study Population Data Collection Fluorosis Data Intraexaminer Reliability Aesthetic Awareness Data Public Water Supplies Analysis and Presentation of Data

Results ............................................................................. 65

Introduction

Dental Fluorosis Results obtained for Fluorosis in 5 year old Gozitan School Children Results obtained for Fluorosis in 12 year old Gozitan School Children Results obtained for Intraexaminer Reliability Aesthetic Awareness Fluoride Availability

Discussion and Conclusions ................................................... 75

Fulfilment of the Study Objectives

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5.1.1

5.1.2

5.1.3 5.1.3.1

5.1.3.2 5.1.4

5.2

Chapter 6

Determination of Prevalence of Dental Fluorosis in the Deciduous Dentition How large a Public Health Problem is Dental Fluorosis in Gozo Currently? Monitoring Trends of Dental Fluorosis How will the New Water Supply System affect Oral Health in Gozo in the Future? Impact on Dental Caries Determination of Aesthetic Awareness of Changes Associated with Dental Fluorosis in the 12 year old children Limitations of the study.

Recommendations ............................................................... 87

Appendix 1 Definitions ............................................................................ 90 Appendix 2 Request for Research in State Schools .............. , ....................... 91 Appendix 3 Letter from University Research Ethics Committee ..................... 93

References ....................................................................................... 94

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LIST OF TABLES

1 Gozo Water Quality Zones ............................................................... 15 2 Tentative estimates of a number of people throughout the world using various .. 26

types of fluoride therapy and preventive measures. 3 Degrees of potentially toxic ingestion offluoride ..................................... 37 4 Primary teeth chronology ................................. '" ............................ 40 5 Permanent teeth chronology .............................................................. 40 6 Comparison of characteristics of Dental Fluorosis and Non- Fluoride EnameL. 53

Opacities. 7 Clinical criteria and Scoring for the TF Index ......................................... 62 8 Levels of Dental Fluorosis in 12 year old children in 1986 .......................... 66 9 Fluoride levels in water by locality in Gozo ........................................... 74

LIST OF FIGURES

1 Map of the Maltese Islands ............... " ......................................... , .... 7 2 Map of Gozo Localities with respective population size according to 2005 ........ 9

Census. 3 DMF-Tin 12 year old children in European Countries for 2004 ................... 14 4 21 US cities study: Fluorosis at age 12-14, according to natural water fluoride .. 23

concentration. 5 Mild Fluorosis .............................................................................. 43 6 Mild to Moderate Fluorosis .............................................................. 43 7 Moderate to Severe Fluorosis ............................................................. 44 8 Severe Fluorosis ....................................................... , ..................... 44 9 TF scores in 5 year old Gozitan School Children ................. " ................... 68 10 TF scores in 12 year old Gozitan School Children .................................... 69 11 Mean TF Scores with their confidence intervals by Locality ......................... 70 12 Map ofGozo showing Mean TF scores by Locality ................................... 71 13 Graph showing correlation between Fluoride concentration and TF scores by ... 73

locality. 14 Breakdown of response as to use of toothpaste from the National Oral Health ...... 80

Survey of the Maltese Islands carried out by Portelli and Vassallo in 2004. 15 DMF-TinS and 12 year olds against Fluoride in water in the Maltese Islands ...... 82

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CHAPTER 1 INTRODUCTION

1.1 BACKGROUND INFORMATION: GOZO

1.1.1 GENERAL COUNTRY INFORMATION

The Maltese archipelago consists of three inhabited islands; Malta, Gozo, Comino (which is

largely uninhabited) and two other uninhabited islands (Fig. 1). They lie in the middle of the

Mediterranean sea with Malta 93 kilometres south of Sicily and 288 kilometres north of Africa

with a total area of 316 square kilometres, (Malta 246, Gozo 67, Comino 2.7).

o I o

ed#erranean Sea

<1 8km I

4

' .

Med terranean Sea

,.,. Marsaxlokk. J,

~_.~~Bbbuga .~ ~} ~"--"'''''-,.

C

Filfl8

Figure 1: Map of the Maltese Islands.

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The population of the Maltese islands at the end of 2005 was estimated at 404,039, with 31,

031 living in Gozo and 8 in Comino. The population is increasing at a steady rate and it is

projected that by the year 2025 it will exceed 418,000 people. Malta has a population density

of 1,513 residents per square kilometre whilst Gozo and Comino have a population density of

452 residents per square kilometre. (NSO 2005)

Compared to the EU, Malta's population is still relatively 'young'. The proportion of the

population under 25 years of age is 31.5 per cent, compared to 29.1 per cent across the EU.

However, 20.3 per cent of the Maltese population is aged between 50 and 64 years, this

being significantly higher than the EU average of 17.9 per cent Hence, within the next ten

years or so, most of the persons within this age cohort will be over 65 years. Assuming that

current socio-demographic trends continue in the future, the main characteristics being a

declining fertility rate and a low immigration intake of younger persons, a steady increase

in the old-age-dependency ratio is expected in the coming years. (NSO 2005)

The climate is warm, with mild wet winters and hot dry summers. There is no fog, snow or

frost Rain falls only for short periods, generally between September and April, and averages

578 mm a year. The average winter temperature is 14 degrees centigrade, whilst in the

summer it is 32 degrees.

1.1.2 POLmCS

Politically, Gozo and Comino form one of the thirteen electoral districts of the Republic of.

Malta. Five representatives are elected to the Maltese parliament, and to better look after

the Gozitan people's interests, one of these is always a central government cabinet minister.

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Besides, each of the fourteen localities or village communities has their own local council

and therefore their mayor. A map of Gozo subdivided into the fourteen localities and their

respective populations is shown in Figure 2.

.GHARB POp!Laton: 1.195

·ZEBBUGAND MARSALFORN Popli'ator.: c.n3

.GHASRI Popu:atDn: 398

• SAN LAWRENZ

·XAGHRA Poptrat:on: ~.C23

-KERCEM • NADUR

PODu!aton: 'i.S&:. . "RABAT (VICTORIA)

Popu:atcon: 6.832

-FONTANA Populaton: 896

• MUNXAR AND XLENDI Popu:aoon:834 • XEWKlJA

·SANNAT Popu'at'Of1: 1.832

• GHAlNSIELEM Popu'at-on :2.671

+QAlA Popt;!at'on: 1.727

Figure 2: Map of Gozo Localities with respective population size according to 2005 Census

1.1.3 EDUCATION

A comprehensive state system provides all levels of education, free at the point of delivery.

This system is complemented by schools run by the church. There are no schools run by

private concerns in Gozo. Schooling is compulsory between the ages of 5 and 16. State

primary schools are found in most towns and villages while all the secondary schools can be

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found in Rabat, the capital city. The data from the 2005 census shows that the illiteracy rate in

Gozo was 11.24%.

1.1.4 THE HEALTH CARE SYSTEM IN GOZO

1.1.4.1 OVERVIEW

In The Maltese Islands, there is a comprehensive national health service that is available to all

Maltese residents and is entirely free at the point of delivery. The Government health services

are funded from general taxation. All residents have access to preventive, investigative,

curative and rehabilitative services in Government health centres and hospitals.

The Government's health centre system works side by side with a thriving private sector.

Secondary and tertiary care is provided principally from two public general hospitals, one in

Malta and one in Gozo, and other supporting specialized hospitals (Oncology, Psychiatric and

Geriatric). There are also two private hospitals, one of which has a branch in Gozo but which

does not supply dental care.

Currently only about 10010 of manpower resources are allocated to preventive examinations,

education and health promotion (Human Resources Department Ministry of Health).

However, several preventive programmes are run on a national scale, such as the free

immunization programme, which covers a wide range of illnesses.

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1.1.4.2 DENTAL CARE SYSTEM

Dental care is provided within the national health system provided by the Government to all

citizens on the basis of equity. There is ease of access to all sectors of the community

irrespective of means in respect of all urgent dental care as well as diagnostic care, preventive

care and oral surgery (Department of Health, Malta 1986). Those who qualitY on a means test

(low income groups), and hospitalized patients are eligible for free restorative care. In addition

children aged between 5 and 15 years enjoy free comprehensive dental care. In Gozo all dental

care provided by the government is carried out at Gozo General Hospital.

1.1.4.3 HUMAN RESOURCES

At present in Gozo there are two dental surgeons employed by Gozo General Hospital. There

are 7 private dental clinics and 12 registered dental surgeons in Gozo. There has been some

level of loss of personnel due to migration to other European countries but not to the extent

that the dental sector in Malta has been affected. This has become an issue due to the disparity

in working conditions between different European countries.

1.1.4.4 FINANCING

Provisional estimates for 2006 indicate that Malta's Gross Domestic Product stood at Lm 2.1

billion (€4.9 billion), or Lm 5,176 (€l2,058) per capita. 8.8% of GNP was spent on healthcare

in 2004. An estimate ofO.4 % of GNP was spent on Dentistry.

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1.1.5 GENERAL HEALm

The health of the Maltese population compares favourably, in broad tenns, with that of other

Western European countries as measured by international indicators such as the WHO's

European Regional Health Indicators (Health Vision, 2000). Infant mortality rate is 3.82 per

1000 live births (2007) and maternal death is a rarity.

There has been a sharp drop in the standardized death rate from all causes since the early 80's.

In the case of premature deaths the rate has fallen below the EU average (Department of

Health, 1995).

The major contributor to mortality and morbidity in Malta and Gozo for the past four decades

has been circulatory disease, 44.3% of deaths in 2005, many due to coronary artery disease

and stroke. Even though the rate is below the European average, it is still well above that of

many neighbouring Mediterranean countries.

Both genetic and lifestyle factors probably contribute to this situation. Risk factors such as

diabetes, obesity, hypertension, and lack of exercise, are all highly prevalent in the Maltese

Islands. Significant differences now exist between the Maltese nutritional pattern and the

traditional 'Mediterranean diet' (Department of Health, 2(05).

Malignant neoplasms also dominate the mortality data (26.8% in 2(05). In men, the leading

causes of death were cancer of the lung, digestive system and prostate, while in women the

commonest killers were cancer of the breast, the colon, the pancreas and the lung (Department

of Health, 2005).

Other significant causes of mortality are due to respiratory system diseases, diabetes and other

metabolic diseases, digestive system disease and accidents (Department of Health, 2(05).

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Infectious diseases are no longer common in the Maltese islands. Various types of viral

hepatitis are endemic, though tuberculosis and measles are on the decline. mv infection

prevails though not in alanning figures. It is estimated that there are about 206 seropositive

mv individuals and cumulative notification of AIDS from 1986 to 2003 is around 47.

1.1.6 ORAL HEALTH

The prevalence of dental caries is low. The mean DMF-T (Decayed, Missing and Filled Teeth)

of the Maltese Islands in 12 year-old school children is 1.3 with the DMF-T being 1.4 in Malta

and 1 in Gozo. Thus the Maltese Islands have achieved the WHO Goal of a DMF-T of 3 or

less and the National Goal of a DMFf of 2 or less. The treatment ratio for 12 year old school

children (filled teeth in relation to decayed and filled teeth) has improved from 0.13 in 1987 to

0.44 in 2004. Currently the treatment ratio is higher in Malta (0.45) than in Gozo (0.36)

(portelli and Vassallo 2004).

The difference between Malta and Gozo is more marked in the 5 year old children than in the

12 year old children. The mean DMF-T in 5 year old school children is 2 with a DMF-T of 2.4

in Malta and 0.7 in Gozo. The WHO goal of having 50% of5 year old school children caries

free has been met, but the National Goal of having 60% of 5 year old school children caries

free has not been met. The treatment ratio for the 5 year old children is very low, with 5.2% of

decayed deciduous teeth being filled in Malta and a negligible amount being filled in Gozo

(portelli and Vassallo 2004). Figure 3 shows a comparison ofDMF-T values for 12 year old

children in European countries for the year 2004. This shows that the DMF-T value for Malta

(1.4) is well below the European mean of 1.93.

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30% of 12 year old school children have poor oral hygiene. Only 5% had no plaque and

therefore good oral hygiene (portelli and Vassallo 2004). Data on levels of periodontal disease

are less recent with the only data available being from the 1987 pathfmder survey carried out

by Moeller which gives the periodontal status in 35-44 year old persons. This data shows a

high prevalence of poor oral hygiene with 78.3% of the sample studied having presence of

calculus, 17.1 % having shallow periodontal pockets and 2.1 % having deep periodontal

pockets. Although the situation of oral hygiene is improving, this remains a problem. The

prevalence of oral malignant lesions has always been low and is stable at 0.1 %

(Histopathology Department SLH).

UK Sweden

Spain

Slovenia

Romania

Portugal

Poland

Netherlands

Malta

Lithuania

Latvia

Italy

Ireland

Iceland

Hungary

Greece

Germany

France

Finland

Denmark

Czech Rep

Cyprus

Bulgaria

Belgium

Austria

0.00

I

I

0.50

0.80

1.00

1.3

I 1.50

1.00

1.30

1.13

1.10 I

1.50

.98

1.23

1.20

0.80

1.14

1.1 0

I 1.04

1.00 1.50

I

1.70

3.50

2. 0

3.50

3.30

2.20

2.50

I 3.03

2.00 DMF-T 2.50 3.00 3.50

Figure 3: DMF -Tin 12 year old children in European Countries for 2004. From the Database o/Oral Health Care in Europe (CECDO).

4.10

4.00

14

4.50

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1.2 WATER SUPPLIES

The Water Operations Unit is responsible for all distribution and ground water operations in

the Maltese islands. These responsibilities include the Water Quality Zones and the

Distribution Control Section. The water supply network is divided into twenty Water Quality

Zones in Malta and Gozo. Each zone is linked to a particular reservoir which is numbered the

same as the Water quality zones. There are five Water Quality Zones for Gozo (15, 16, 17, 18,

and 19) which supply the localities as shown in Table 1 (WSC- Institute for Water

Technology).

• ">,:,;., (~,!~;' ~)5"U;·1~~I~·;t¥:·~<j~ &;(~~~\;~¥.ri~;R;~:.(~~iE ~i~"";i.i;;'; .:}~,~c"· ;j~~t;.~f~

MUNXAR 15 SANNAT 15 XLENDI 15

FONTANA 16 VICTORIA (UPPER) 16 XEWKIJA (LOWER) 16

GHARB 17 GHASRI 17 KERCEM 17

MARSALFORN 17 VICTORIA (LOWER) 17

SAN LAWRENZ 17 XEWKIJA (UPPER) 17

ZEBBUG 17 GHAJNSIELEM 18

MGARR 18 QALA 18

XAGHRA 18 NADUR 19

Table 1: Gozo Water Quality Zones. (Institute for Water Technology)

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In 2005-06 the WSC produced just under 31 million cubic metres (culmt) of potable water in

Malta & Gozo. Approximately 13.4 million (43%) culmt. were produced from various

groundwater sources, the main one being Ta' Kandja Pumping Station which is a series of

underground galleries some 81an in length, 100m below ground. Groundwater production,

however, is not enough to meet demand which means that the Corporation has to convert

seawater into high-purity drinking water in its three RO plants at Pembroke, Cirkewwa and

Ghar Lapsi and blend it with groundwater. Moreover, the underground water table is affected

by illegal extraction, causing its salinity to rise to unacceptable levels, which has forced the

WSC to increase RO water production. This allows it to reduce groundwater production as a

percentage of overall water production. In 2005-06 approximately 17.4 million (57010) culmt.

of water was produced by RO plants.

This blend is stored in the 24 reservoirs in Malta, Gozo and Comino which have a total

capacity of 400,000 cubic metres. All the production, transfer and storage of water is

controlled and monitored in real time by remote sensing from the Control Room based at

Luqa. Reservoir levels, flow rates and pressures are kept at optimal operating parameters at all

times. The water distribution system is a vast and complex network: of over 2136 Ian of

pipes, pumps, reservoirs, automated and manual valves and other components. This network:

leads to approximately 142,000 water service connections to homes, businesses, industries,

hotels, schools, etc., serving over 400,000 persons throughout the Maltese Islands (WSC).

In the past the Maltese Islands had naturally present fluoride in the water supply, which never

exceeded the maximum of 1.4ppm. When reverse osmosis plants were introduced in Malta in

the early 199Os, the levels of fluoride in the polished water produced by the reverse osmosis

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plants decreased to the negligible amount of less than 0.2 ppm. This led to Malta not being

exposed to sufficient fluoride to produce dental fluorosis.

In Gozo, water supplied to households in the past was all ground water pumped from bore

holes, with different areas in Gozo getting water from particular bore holes. This water

contains high levels of fluoride ranging from 1 ppm to 2.2 ppm. The Gozo system also used to

supply water to Rabat in Malta.

In 2004 a new system using a reverse osmosis polishing plant was introduced in Gozo. This

was done so that all the ground water in Gozo will be either polished or blended with polished

water. This is mainly done by using a Collection Scheme where ground water from all the

bore holes is pumped to one reservoir. A part of the ground water is introduced into one of the

three reverse osmosis plants and polished. This water is then blended with another two parts of

non- polished ground water and this mixture is then stored in the water quality zone reservoirs

and from there pumped to the households in Gozo. The polished water produced by reverse

osmosis plants contains less fluoride than the ground water and thus this new system produces

water which meets EU drinking water regulations parameters (personal conversation with Mr.

Anthony Rizzo, fonner CEO ofWSC).

In the Maltese Islands, water for public consumption is required to meet the standards set out

in European Legislation. The drinking water directive (98/83/EC) puts the limit for fluoride in

drinking water at 1.5 mg/l (1.5ppm). This directive was transposed into Maltese Law LN

23/2004 which came into force in January 2004. This was amended by LN 11612004 due to

the introduction of the Annexes. The parameter for fluoride had to be corrected to below

1.5mg/l in accordance with the relevant legal notice by 31 December 2005.

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Fluoride analysis is perfonned by the Warer Services Corporation as part of their check and

audit monitoring in order to meet the requirements of LN 2312004 and 116/2004. Fluoride

levels are analysed at the village points twice a year for Maltese villages and on a monthly

basis in the case of Gozo villages. The results are read using UV MS spectrophotometry. The

WSC is undergoing a Drinking Warer Quality Project (funded by EU) which consists of the

refurbishing and upgrading the existing RO plants to improve the quality of drinking warer at

the consumers' tap. It is planned to increase the pumping from reverse osmosis plants and

decrease that from ground water to improve the quality of ground water. This would result in a

further reduction in the fluoride concentration in both Malta and Gozo (WSC- Institute of

Water Technology)

1.3 AIM AND OBJECTIVES

1.3.1 i\l1v.l

The aim of this study was to examine the levels of dental fluorosis in 5 year old and 12 year

old school children, so as to evaluate if dental fluorosis in Gozo is presently a public health

problem.

A path finder survey carried out in 1986 by Moller suggests that there was a public health

problem since values of >0.6 using Dean's index were recorded. These exceeded the

threshold value of 0.4-0.6. However, Moller himself questioned the results due to the

possibility that other enamel opacities were included as dental fluorosis.

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1.3.2 OBJECTIVES

The objectives of this study were:

1 To determine prevalence of fluorosis in the deciduous dentition in Gozo, which has

never been determined previously.

2. To establish how large a public health problem dental fluorosis currently is in both

the deciduous (in 5 year olds) and the permanent dentition (in 12 year oIds) in Gozo.

3. To determine how aware the 12 year old Gozitan children are about the aesthetic . changes to their upper central incisors, associated with dental fluorosis.

4. To serve as a comparison for future studies which may be carried out to determine

the effect of polished water on fluorosis prevalence in the same population.

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CHAPTER 2 LITERATURE REVIEW

INTRODUCTION

For more than a century, fluorides have been used to prevent dental caries. Although it is

scientifically proven that small concentrations of fluoride can significantly reduce dental caries

without any ill-effects, the usage of fluoride is still regarded as a controversial issue and is still

being researched.

2.1 FLUORIDES IN THE ENVIRONMENT

Fluorine is one of the most reactive elements and therefore, is rarely encountered in nature in

its elemental form. Combined chemically in the form of fluorides, the fluoride ion is the

thirteenth most abundant element, representing about 0.06 - 0.0<J01o of the Earth's crust.

Although there is an obvious abundance of Fluoride, it is negatively charged and thus

combines with positive ions to form stable compounds (e.g. calcium fluoride and sodium

fluoride) (MMWR Guidelines, 200 I) and is therefore not biologically available in its

elemental form.

2.1.1 THE CHEMISTRY OF FLUORIDE IN WATER

Fluoride occurs naturally in all water supplies. Artificial water fluoridation is the process of

adjusting the naturally occurring fluoride in water supplies to a level that is known to

benefit teeth.

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Due to the presence of fluoride in the Earth's crust, water contains fluorides in varying

concentrations. Fluoride is present in water supplies as a result of having been dissolved out

of the rocks and soils over which the water has travelled. There are two normal forms of

fluoride, inorganic and organic; however, in dentistry, medicine and public health, only the

inorganic form (which yields the fluoride ion) is important. Inorganic fluoride also occurs

in two different forms: ionic fluoride, and nonionic fluoride. Importantly however, it is the

concentration of ionic fluoride in solution that is referred to (generally in parts per million -

ppm) when we talk of the fluoride concentration of a water supply. The concentration of

fluoride in water is analysed by the fluoride ion specific electrode which measures free

fluoride ions, not fluoride bound to metal ions such as calcium, magnesium, iron or

aluminium (Fejerskov et al 1996). The natural fluoride concentration of ground water is

affected by the availability and solubility of fluoride-containing minerals and the porosity

of rocks and soils over which the water passes, in addition to temperature, pH, and the

presence of other minerals such as calcium, aluminium and iron which may combine with

the fluoride ion. Ground waters in the United States have been reported to have fluoride

concentrations of up to 67 parts per million, and in parts of India and Africa much higher

concentrations have been reported (Fejerskov et alI996).

Waters with high fluoride content are usually found at the foot of high mountains and in areas

with geological deposits and ground waters. The natural concentration of the element in

ground water depends on such factors as the geological, physical and chemical characteristics

of the water supplying area, the consistency of the top soil, the porosity and permeability of

the aquifer rocks and the pH and temperature of the water. Owing to these factors, fluoride in

ground water fluctuates within wide limits - from <1 to >25 ppm. In surface fresh water,

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which is less influenced by fluoride- containing rocks, the fluoride content is usually low -

0.01 to 0.3 ppm. Fluoride concentrations are higher in sea than in fresh water, averaging 1.3

ppm (Murray, 1986).

2.2 FLUORIDE VEIDCLES

Categorizing fluoride compounds into systemic and topical fluorides is not easily done; the

line between these categories gets blurred; some systemic vehicles have a topical effect and

some topical vehicles can inadvertently have systemic effects. The various vehicles available

can be categorized into three: population measures, individual measures and professionally

applied measures.

2.2.1 POPULATION MEASURES

A population measure is a group approach to the problem with little choice available to the

public. This includes:

- Water fluoridation, which is the addition of fluoride to the public water supplies;

- School-water fluoridation, which is the addition of fluoride to the school-water supply;

Determination of the most appropriate levels of fluoride in drinking water is crucial if the

measure is to be both effective and to receive public acceptance. This knowledge is important

both for communities intending to begin fluoridation, and for those with excessive natural

fluoride which require partial defluoridation.

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Early studies of the relationship between fluoride concentration in drinking water, mottled

enamel, and dental caries were carried out by Dean. His aim was to find out the 'minimal

threshold' of fluoride - the level at which fluoride began to 'blemish the teeth'. He showed

conclusively that the severity of mottling was positively correlated with the fluoride

concentration in the drinking water (Dean, 1936). He presented evidence to show that if the

concentration of fluoride did not exceed 1 ppm there was no public health significance. The 21

city study showed that near maximal reduction in caries experience is seen with a

concentration of 1 ppm fluoride in the drinking water (Dean et aI., 1942 Figure 4). At this

concentration, fluoride caused only 'sporadic instances of the mildest forms of dental fluorosis

of no practical aesthetic significance'. Mottling of teeth began to be noticeable when the

fluoride concentration increa')ed above 1.5 ppm. Dean's original observations have been

substantiated by a number of investigators.

100 90 80 70

~60 Iso w

.~ 40 ;; v

30 20 10

Al 1 ppm maxim"", reduction in dental .jecay ! oo minrnal

fluorosis I I

OJ-.-,......,.--r-T""""'!"'"......,..~ ...

o 0 0'> 0'> 0" Ot' 0" ~~" y'" 'Vfo

12

10 Questionable

8 _Very Mild ~ _ Mild

6 2 ii: DModerab!

4 Severe --DMFT

2

o

Figure 4: 21 US cities study (Dean et aI1941-42): Fluorosis at age 12-14, according to natural water fluoride concentration (ppm).

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The optimal range of community water fluoridation (optimal with respect to near maximal

dental caries prevention and minimal risk of enamel fluorosis) had previously been determined

to be 0.7 - 1.2 ppm, based on studies of fluid consumption according to the annual average of

the maximum daily air temperature. Failure to make adjustment for this factor may result in a

higher prevalence of fluorosis in warmer climates where more water is consumed. The

optimum caries-protective effect of different fluoride concentrations have been demonstrated

in hot climatic zones (0.6 ppm) and in cold zones (1.0-1.2 ppm). These standards are,

however, not appropriate for all parts of the world such as the tropical and sub-tropical areas.

Thus the level of 1.0 ppm has been viewed as an upper limit, even in a cold climate, and 0.5

ppm, now used in Hong Kong and recommended in the Gulf states, may be a more appropriate

lower limit (WHO, 1984).

The Forum on Fluoridation (Ireland 2002) has recommended that the optimal level of fluoride

in drinking water should be redefmed from the present level (0.8 to 1 ppm) to between 0.6 and

0.8 ppm, with a target value of 0.7 ppm after having taken into account the increase in the

major potential sources of fluoride intake.

2.2.2 INDIVIDUAL MEASURES

An individual measure offers the public a degree of choice. These measures however do not

necessitate utilization of health services. These are:

- Fluoridated toothpastes *

- Salt fluoridation

- Bottled water fluoridation

- Milk fluoridation

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- Fluoride tablets and drops

- Fluoride mouthrinses

- Individually applied gels

*Fluoridated toothpaste contributes to the risk of enamel fluorosis since the swallowing reflex

of children aged less than six years is not always well controlled, particularly among children

aged less than three years (Nacacche et al 1992, Simard et al 1991). Children are also known

to swallow toothpaste deliberately when they like the taste. These reasons are why high

concentration fluoride toothpastes (1,500 ppm fluoride) are contraindicated for children less

than six years of age. Supported by more than half a century of research, the benefits of

fluoride toothpastes in preventing caries are firmly established (Marinho et al 2(03).

2.2.3 PROFESSIONALLY APPLIED MEASURES

Professionally applied measures also offer the public a degree of choice. However, they

require utilization of services. These include:

- Topical applications - fluoride gels, solutions and varnishes

- Prophylaxis paste

- Sequential rinses

- Slow release fluorides

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2.3 FLUORIDE USAGE

Fluoride is being used widely on a global scale, for the most part with great benefits.

Fluoride toothpaste 450

Water fluoridation 210

Dropsffablets 20

Mouthrinses 20

Clinical topicals 20

Fluoridated salt 4.0

School fluoridation 0.2

Table 2: Tentative estimates of number of people throughout the world using various types of fluoride therapy and preventive measures (Murray et oZ., 1991).

2.4 FLUORIDE AS A CARIES PREVENTIVE AGENT

Dental caries is an infectious, multifactorial disease affecting most persons in industrialised

countries and some developing countries (Bratthal et aI, 1996).

The first suggestion of a possible connection between the fluoride ion and the prevalence of

dental caries occurred towards the end of the nineteenth century, when Sir James Crichton-

Browne, (1892) stated " ... .1 think it well worthy of consideration whether the reintroduction

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into our diet of child bearing women and children, of a supply of fluorine in some suitable

natural form .... might not do something to fortify the teeth of the next generation."

Dr. Frederick McKay would appear not to have taken account of Crichton-Browne's words

when he spent almost 30 years searching for the cause of the "Colorado stain" in Colorado

Springs and the surrounding EI Paso county, or "denti di chiaie" in Naples, Italy, before

realizing, in 1931, that the occurrence of mottling, which was localized in definite geographic

areas concomitant with a reduced rate of caries, was due to a high fluoride content in the water

supplies.

"We have discovered the presence of hitherto unsuspected constituents in this water. The high

fluorine content was so unexpected that a new sample was taken with extreme precautions and

again the test showed fluorine in the water" (Churchill, 1931).

Fluoride reduces the incidence of dental caries and slows or reverses the progression of

existing lesions. Although pit and fissure sealants, meticulous oral hygiene and appropriate

dietary practices contribute to caries prevention and control, the most effective and widely

used approaches have included fluoride use. The widespread use of fluorine has been a major

factor in the decline in the prevalence and severity of dental caries in economically developed

countries (Bratthal et ai, 1996). Although this decline is a major public health achievement, the

burden of disease is still considerable in all age groups (MMWR 200 1).

Since many fluoride modalities are effective, inexpensive, readily available and can be used

both in public and private health care settings, their use is likely to continue. Research about

fluorides led to the development of various modes of fluoride use. Different regimes, vehicles

and materials involving fluoride were tested and later applied to increasing groups of

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populations throughout the world, starting from the fluoridation of the piped water supplies in

Grand Rapids, Newburgh and Brantford.

There has been a decline in dental caries prevalence and incidence during the last two decades,

both in the economically developed and in economically developing countries. This decrease

is considered to be largely due to the widespread use of fluoride. (Buzalaf et al 200 1). In a

systematic review of 214 studies on water fluoridation, an increase in the proportion of caries­

free children and a reduction in the number of teeth affected by caries were observed (Mc

Donagh et al 2000).

To develop and apply appropriate and effective caries prevention and control strategies,

identification and assessment of groups and persons at high risk of developing new carious

lesions is essential (Meskin 1995). Caries risk assessment is difficult because it attempts to

account for the complex interaction of multiple factors.

Populations believed to be at increased risk for dental caries are those with low socioeconomic

status or low levels of parental education, those who do not seek regular dental care and those

without access to dental services. Persons can be at high risk for dental caries even if they do

not have any of these recognised factors.

Individual factors that possibly increase risk include active dental caries; a history of high

caries rate in older siblings or care givers; root surfaces exposed by gingival recession; high

levels of infection with cariogenic bacteria; impaired ability to maintain oral hygiene;

malformed enamel or dentine; reduced salivary flow because of medications, radiation

treatment or disease; low salivary buffering capacity and the wearing of space maintainers,

orthodontic appliances or dental prostheses. Risk can increase if any of these factors are

combined with dietary practices conductive to dental caries (e.g. frequent consumption of

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refined carbohydrates). Risk decreases with adequate exposure to fluoride (Meskin 1995, Pitts

1998).

Children and adults who are at low risk for dental caries can maintain the status through

frequent exposure to small amounts of fluoride such as fluoridated drinking water and using

fluoride dentifrice. Children and adults at high risk of dental caries might benefit from

additional exposure to fluoride such as fluoride supplements and professionally applied

products.

2.5 EFFECT OF FLUORIDE - MECHANISM OF AcrION

An understanding of the mechanism of action of fluoride is clearly important to ensure its

appropriate use as a caries preventive agent (Clarkson, 1991). The exact mechanism of action

through which fluoride impacts on caries is not fully understood although a consensus has

emerged in recent years. Fluoride can impart a cariostatic effect by different mechanisms,

depending on the amount of fluoride present at the enamel-plaque interface (Margolis and

Moreno, 1990).

The two main hypotheses which have been proposed to account for the anti-caries effect of

fluoride are through a pre- and post- eruptive effect. These can be divided into a number of

mechanisms.

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2.5.1 PRE-ERUYfIVE EFFECT

* by promoting the growth of larger and more perfect crystals;

Fluoride is incorporated into enamel during tooth formation producing a more perfect crystal,

with a lower carbonate content, which is consequently more resistant to acid action; crystals

tend to dissolve in areas of imperfection. The pre-emptive benefits may be especially

important for reducing pit-and-fissure lesions (Groenveld et aI., 1990).

2.5.2 POST-ERUPTIVE EFFECT

* CrystaHization;

By reducing the rate of dissolution of enamel in acids through incorporation of fluoride ions

into the apatite lattice - fluoride and hydroxyl ions have the same charge, and they can

interchange converting hydroxyapatite into fluoridated hydroxyapatite. The latter mineral is

both more stable and acid resistant than pure hydroxyapatite. This mechanism could also act

pre-eruptively (Burt & Eklund, 1992). However, it is important to note that relatively high

concentrations of fluoride within the enamel are required for a significant reduction in enamel

solubility to result. The evidence is contradictory on whether the concentration of fluoride in

sound enamel is sufficient to reduce its solubility (Murray et aI., 1991). Levine (1976) argues

that a high concentration of enamel fluoride could not by itself explain the extensive

reductions in caries that fluoride produced.

*inhibition of the e1l1.3me system of acid producing bacteria;

Fluoride in plaque inhibits glycolysis, the process by which sugar is metabolized by bacteria to

produce acid. The main site of fluoride inhibition is in the Emden-Myerhof pathway of acid

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production, by its action on enolase, the enzyme that converts phosphoglyceric acid to

phosphoenolpyruvic acid. When this reaction is blocked, phosphoglycerate accumulates and

later products, such as phosphoenolpyruvate (PEP) and lactic acid, are not fonned. This has

several consequences when it occurs in plaque:

1. The reduced production of1actate obviously impairs the ability of the bacterial plaque

to cause caries (Murray et al., 1991).

2. In many bacteria, the uptake of glucose requires the presence of PEP, so uptake is

reduced by fluoride (Hamilton, 1977).

3. The reduced glucose uptake prevents the synthesis of glycogen; the intracellular

polysaccharide that acts as a store of carbohydrate and makes it possible for oral

bacteria to continue to produce acid after the dietary sugar has been washed away by

saliva (Murray et al., 1991).

4. Fluoride reduces the pH within the bacteria (by dissociation ofHF) - this increases the

W concentration in the cell and this may reach a level so far removed from the

optimum pH of the enzymes that acid production is reduced or may even cease

(Eisenberg and Marquis, 1980).

Many bacteria are more sensitive to fluoride at low pH levels. It has been suggested that

fluoride reduces their acidurity. The latter depends on the bacteria's power to extrude It" from

the cytoplasm, a process that requires ATPase enzyme. This enzyme is very sensitive to

fluoride in S. mutans. Marquis, (1990) suggested that fluoride in plaque may inhibit this

ATPase leading to a build up of acid which in tum inhibits enolase and other enzymes. In

many cases, enzymes have metal ion co-factors (example Fe2+ or Fe*) and the fluoride ion

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binds to these ions and stops the co-factors from working. However the enzymes that do not

have metal co-factors are still inhibited. Thus, there must be another mechanism of action.

There is also evidence that plaque fluoride can inhibit the production of extracellular

polysaccharide by cariogenic bacteria, a necessary process for plaque adherence to smooth

enamel surfaces (Hamilton, 1990). There is, however, a lot of contradiction regarding this

process (Murray et al., 1991).

* By changing the balance between dissolution and precipitation in caries lesions towards

precipitation.

Fluoride can act as a catalyst in the precipitation of hydroxyapatite. The ionic fluoride in the

aqueous fluid of the plaque and among the crystals within the enamel or dentine encourages

the repair of the early carious lesion by reprecipitation of the enamel crystals shifting the

demineralizationlremineralization equilibrium towards mineralization. The reSUlting inhibition

of demineralization and/or the enhancement of remineralization can explain the effects of

application of low fluoride concentrations such as from fluoridated drinking water and the use

of fluoride containing dentifrices and mouth rinses (Koulourides, 1990).

In addition to the mechanisms described, high-concentration fluoride gels may have a specific

bactericidal action on cariogenic bacteria in the plaque (Bowden, 1990; Loesche, 1977).

Fluoride action may best be described as reducing lesion progression rather than actually

preventing the initiation of the disease (Clarkson, 1991). The weight of evidence favours the

view that fluoride's most important caries-inhibitory action is post-eruptive, though the

respective roles of pre-emptive and post-eruptive fluoride continue to be debated (Horowitz,

1990; Thylstrup, 1990).

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Current scientific evidence therefore indicates that fluoride works through several

mechanisms. The current opinion is that the solubility - remineralization concept, with its

emphasis on a constant flow of ionic fluoride, is the major effect (Fejerskov et al., 1981).

Because of the various possible mechanisms through which fluoride can have an impact, the

method of delivery is going to be important This in tum will influence the vehicle. The

optimum characteristics for fluoride is a low concentration for as long as possible, a frequent

low dose. This is important to maintain a significant concentration in saliva and plaque fluid

for the control of enamel dissolution. This is important in making the appropriate scientific

choice.

Fluoride exerts its effect primarily through topical action. There is some uncertainty whether

salivary or plaque fluoride is primarily responsible, but the fact remains that the effect is

topical. Although systemic fluoride may be available via the saliva, only local fluoride is

necessary for the success of the process (Leverett, 1992).

2.6 FLUORIDE AND THE BODY

Fluoride is considered to be a 'beneficial element for humans' because of its positive impact on

dental health (National Research Council, 1989), it was once considered to be an essential

nutrient for human growth (National Research Council, 1974). However, available evidence

did not justify classifying fluoride as an essential element by accepted standards (National

Research Council, 1989).

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2.6.1 FLUORIDE INTAKE BY MAN

Because of the environmental presence of fluoride, individuals are exposed to various levels of

intake through foods, water, industrial and phannaceutical products, and other sources.

Waterborne fluoride has been said to represent the largest single source of daily intake of this

ion. The daily amount of fluoride intake through water varies with climate and age of the

individual (Murray, 1986). In some parts of the world, however, staple diets, are particularly

high in fluoride, and this source can be the main contributor. On the basis of extensive analysis

reported by several authors, the total daily fluoride intake by man may vary from 0.2 mg of

fluoride per day in infants to 5.0 mg of fluoride per day in adults. Although there is no

consensus as to the maximum safe daily dosage of fluoride, a total intake of between 0.05 and

0.07 mg FlKg body weight has been suggested (Murray, 1986).

2.6.2 ABSORPTION, RETENTION AND EXCRETION

Ingested fluoride is absorbed mainly from the upper gastrointestinal tract. The process occurs

by passive diffusion. The half-time for absorption is approximately 30 minutes, so peak

plasma concentrations usually occur within 30 to 60 minutes; the time for its occurrence is

independent of the amount of fluoride ingested Absorption across the oral mucosa is limited

and probably accounts for less than 1 % of the daily intake. Absorption from the stomach

occurs readily and is inversely related to the pH of the gastric contents (Whitford, 1990). High

concentrations of dietary calcium and other cations that form insoluble complexes with

fluoride can reduce fluoride absorption from the gastrointestinal tract (Whitford, 1986).

Blood plasma is considered to be the central compartment into which and from which fluoride

must pass for its subsequent distribution and elimination. The scientific literature contains

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rather a wide range, 0.7 - 2.4 IlmoJ/L, for the 'normal' plasma fluoride levels (Myers, 1978;

Guy, 1979). Such wide differences might be due to unrecognized population differences in

fluoride intake, in fluoride metabolism, or the result of problems associated with fluoride

analysis.

Plasma fluoride concentrations rise and fall according to the pattern of fluoride intake. This is

dependant upon the fluoride vehicle used. The rates of absorption, soft tissue distribution,

calcified tissue uptake and renal excretion of fluoride all influence the plasma fluoride

concentration at any given time after fluoride intake. The height of the plasma peak is

proportional to the fluoride dose ingested and the rate of absorption, but is also determined by

the body weight of the subject. The plasma half-life for fluoride in human adults ranges from 4

to 10 hours. A steady state relationship exists between plasma and soft tissue fluoride levels

(Whitford, 1990).

Absorbed fluoride begins to leave the blood within minutes, concentrating in bones and the

kidneys. Of the fluoride absorbed by the young or middle-aged adult each day, approximately

50% will be associated with calcified tissues within 24 hours and the remainder will be

excreted in urine.

2.6.3 FLUORIDE IN TEETH AND BONE

Fluoride has an affinity for the calcified tissues, that is, bone and developing teeth. Fluoride

that is not excreted is deposited in these hard tissues, though storage is dynamic rather than

inert. Bone fluoride levels range from 800 to 10,000 ppm, depending on many factors,

including age and fluoride intake (Wiedmann and Weatherall, 1970; Whitford, 1990). Fluoride

is not irreversibly bound to bone. Fluoride levels in the outer layers of dental enamel range

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from 400 to 3,000 ppm and decrease rapidly with greater enamel depth. Fluoride

concentrations in soft tissue rise or fall parallel to serum fluoride levels, but because the

excretion and deposition mechanisms operate so rapidly there is negligible retention of

fluoride in the fluids of soft tissues other than the kidney (Whitford, 1986).

2.6.4 EXCRETION

The principal route of excretion of absorbed fluoride is by the kidneys via the urine. Excretion

of fluoride in urine begins very rapidly after uptake. Approximately 50010 of the fluoride

absorbed from the gastrointestinal tract of adults each day is excreted in the urine. Some

excretion takes place through sweat and fluoride can also appear in saliva. About 10-25% of

fluoride is not absorbed and is excreted in the faeces. Fluoride crosses the placenta, but it does

not seem to be excreted in milk to any significant extent.

Factors which alter urinary pH may profoundly affect the quantitative features of the

metabolism of the ion (Whitford, 1990). Such factors include the composition of the diet,

certain metabolic diseases such as diabetes mellitus, certain drugs, and the altitude at which

the individual resides.

The importance of renal clearance in the body's regulatory mechanism means that when

kidneys are not functioning properly, the amount of fluoride stored in the body can increase.

Special consideration, with regard to fluoride ingestion, should thus be given to people with

chronic kidney failure. There is, however, insufficient evidence to recommend that all patients

with renal disease drink fluoride free water (Burt and Eklund, 1992).

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2.7 FLUORIDE TOXICITY

Like all other necessary elements fluoride can be toxic at high doses. Table 3 shows the

degrees of potentially toxic ingestion of fluoride.

Acute fatal poisoning, 10 Kg child

Acute fatal poisoning, 3-year old child

Acute fatal poisoning, adult renal dialysis

Short-term nonserious nausea in elementary school children

Severe skeletal fluorosis

Dental fluorosis

Acute fatal poisoning in animals

2.5 - 5.0 g, 2 - 4 hours

320 mg, 2 - 4 hours

--435 mg, ~3 hours

Dialysate fluid 30 - 50 ppm F, for 3 hours

93 - 375 ppm F in drinking water, small amounts

10 - 25 mg F daily, 10 - 20 years

<0.1 mg F /Kg body weight/day during tooth development

~50 mg F/Kg body weight

Table 3: Degrees of potentially toxic ingestion of fluoride (Burt & Eklund, 1992).

2.7.1 ACUTE TOXICITY

A review of the literature reveals a wide range of estimates for the actual lethal dose in

humans. They range from 6-9 mg FlKg (Driesbach, 1980) to over 100 mg FlKg (Lidbeck et

aI., 1943). The 'certainly lethal dose' (CLD) corresponds to a fluoride dose range of from 32 to

64 mg FlKg. While this is important information, it is of limited utility. Of more value is the

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'probably toxic dose' (PTD), which has been defined as "the minimum dose that could cause

toxic signs and symptoms, including death, and that should trigger immediate therapeutic

intervention and hospitalization" (Whitford, 1987). It is concluded, from various reports, that

the PTD is approximately 5 mg FlKg (Dukes, 1980; Eichler et aI., 1982; Horowitz, 1978).

The symptoms associated with acute toxicity include salivation, nausea, vomiting, diarrhoea,

fatigue and cramps. In cases of fatal poisoning, death occurs within 24 hours as a result of

respiratory or cardiac failure.

2.7.2 CHRONIC TOXICITY

The long term ingestion of amounts of fluoride above adequate therapeutic levels will result in

fluorosis.

2.8 FLUOROSIS

2.8.1 DENTAL FLUOROSIS

Dental fluorosis is defined as a permanent hypomineralization of enamel, characterized by

greater surface and subsurface porosity than in normal enamel, resulting from excess fluoride

reaching the developing tooth during developmental stages (Fejerskov et aI., 1990).

Several different factors may result in changes in the normal appearance of the enamel (Small

and Murray 1978, Pindborg 1982). The single most studied causal factor is fluoride which can

result in a range of clinical manifestations referred to collectively as dental fluorosis. This

condition can be distinguished from other defects of the enamel based on enamel colour,

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distribution of the condition on the affected tooth or within the mouth, and the extent to which

the enamel is left intact (Rozier 1994).

Enamel changes in populations exposed to differing levels of fluoride were first described by

McKay in his initial publication with black (McKay and Black, 1916). A precise description

was provided by McKay (1929) in a subsequent paper, in which he stated, " there are all

gradations, from the merest flecking of certain teeth, with white spots scattered about

otherwise normal enamel, to other conditions in which the entire enamel structure is uniformly

dead paper white, with or without the presence of the brown discoloration; and still others in

which there has been the most pronounced gross destruction of the enamel surfaces by what

may be called, for want of a better tenn, corrosion."

Severe forms of dental fluorosis can occur only when young children ingest excess fluoride,

from any source, during critical periods of tooth development. Tables 4 and 5 show the

chronology of tooth development in the deciduous dentition and pennanent dentition

respectively. The occurrence of enamel fluorosis is reported to be most strongly associated

with cumulative fluoride intake during enamel development, but the severity of the condition

depends on the dose, duration, and timing of fluoride intake (Larsen et aI., 1987). The

mechanism underlying the development of dental fluorosis has not been conclusively

determined. In the past it was believed that the excessive fluoride intake interfered with the

function of ameloblasts, perhaps inhibiting the secretion of, or altering the composition of the

enamel matrix proteins. This now appears unlikely for several reasons including the fact that

the risk of dental fluorosis is lowest during the secretory stage of enamel development

(Fejerskov et all996).

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3rd-5th month in utero

Age 4-5 months

Age 6-8 months

5th month in utero

Age 9 months

Age 16 -20 months

5th month in 6th-7th month in utero utero

Age 6 months Age 10-12 months

Age 12-16 Age 21-30 months months

Table 4: Primary teeth (deciduous dentition) chronology.

u L u L u L u L

3--4m 3--4m 10-12m 3-4 m 4-5m 4-5m Birth Birth

4-5y 4-5y 4-5y 4-5y 6-7y 6-7y 2.5-3y 2.5-3y

7-8y 6-7y 8-9 Y 7-8y 11-12 Y 9-10 Y 6-7y 6-7y

Table 5: Permanent teeth chronology

Microscopically, the structural arrangement of the crystals appears normal, but the width of

the intercrystalline spaces is increased, causing pores. The degree and extent of porosity

depends on the concentration of fluoride in the tissue fluids during tooth development

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(Fejerskovet alI990). In fact, the risk of dental fluorosis, based on animal studies, is directly

related to the interaction of the circulating fluoride concentrations and the time, that is, the area

under the time-concentration curve. Thus it appears that dental fluorosis can result from a

range of plasma fluoride concentrations provided that they are maintained for sufficiently long

periods (Whitford 1997). With increasing severity of fluorosis, the fluoride concentration

throughout the enamel, the depth of enamel involvement, and the degree of porosity also

increases (Fejerskov 1990).

Fluorosis is less prevalent and less apparent in primary teeth than in pennanent teeth, and, in

any case, fluorosis of the primary teeth has only short- tenn rather than long-tenn

consequences (BuzaIaf 200 1). Therefore the major concern about fluorosis is in the permanent

dentition, particularly with maxillary incisors.

Evidence suggests that 0.03 to 0.1 mg FlKg body weight as the borderline zone at least for

European children (Fejerskov et aI., 1987). Studies in Kenya have found fluorosis with

average intakes as low as 0.03 mg FlKg body weight (Baelum et al., 1987). Further research is

thus needed in this area. Research evidence also suggests that periodic 'spikes' of high F in

plasma are more likely to produce fluorosis than a consistent day-to-day intake (Burt and

Eklund,1992).

The post- secretory and early maturation stages of enamel development appear to be most

susceptible to the effects of fluoride (DenBesten PK, Thariani H.1992); these stages occur at

varying times for different tooth types. For central incisors of the upper jaw, for example, the

most sensitive period is estimated at age 15-24 months for boys and age 21-30 months for

girls (DenBesten PK, Thariani H.I992, Evans RW, Stamm JW 1991).

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Other factors that may increase the susceptibility of individuals to dental fluorosis are altitude

(Angrnar Mansson, Whitford 1990, Maybelya 1992, Whitford 1997 , Yoder 1998), renal

insufficiency (Juncos 1972, Kaminsky 1990, Porcar 1998, Turner 1996) and malnutrition

(Rugg-Gunn et al 1997 , Yoder 1998). Some of these factors, however, can produce enamel

changes that resemble dental fluorosis in the absence of significant exposure to fluoride.

Studies of dental fluorosis, done in areas with 8.I,d witt'iout fluoridated dr.r.king water, have

identified four major risk factors: use of fluoridated drinking water, fluoride supplements,

fluoride dentifrice and infant formulas before the age of seven years. Some manufactured

children foods and drinks may also be important contributors to total daily fluoride intake

(Buzalaf et aI2001).

Concerns regarding the risk for enamel fluorosis are limited to children aged <6 years with the

most critical period for developing fluorosis on the permanent central incisors estimated to be

between 22 to 25 months of age (Evans and Darvell 1995). The enamel is no longer

susceptible once its pre-emptive maturation is complete. Children aged >6 years are

considered past the age that fluoride ingestion can cause cosmetically objectionable fluorosis

because only certain posterior teeth are still at a susceptible stage of enamel development, and

these will not be readily visible.

In addition, the swallowing reflex has developed sufficiently by age 6 years for most children

to be able to control inadvertent swallowing of fluoride toothpaste and mouthrlnse.

The very mild and mild forms of enamel fluorosis (Figure 5) appear as chalklike, lacy

markings across a tooth's enamel surface that are not readily apparent to the affected person or

casual observer. In the moderate form, >50% of the enamel surface is opaque white (Figure 6).

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Figure 5: Mild Fluorosis (by Elke Babiuk adapted from http://fluorideaiert.org/dentai­fluorosis.htm )

Figure 6: Mild to Moderate Fluorosis (by Elke Babiuk adapted from http://fluorideaiert.orgidentai-fluorosis.htm )

The rare, severe form of dental fluorosis manifests as pitted and brittle enamel (Figure 7 and

Figure 8). After eruption, teeth with moderate or severe fluorosis might develop areas of

brown stain. In the severe form, the compromised enamel might break away, resulting in

excessive wear of the teeth.

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Figure 7: Moderate to Severe Fluorosis (by David Kennedy adapted from http://fluoridealeI1.orgldental-fluorosis.htm )

Even in its severe form, enamel fluorosis is considered a cosmetic effect, not an adverse

functional effect (Kaminsky et al1990, Clark et aI1993). Some persons choose to modify this

condition with elective cosmetic treatment.

Figure 8: Severe Fluorosis (by Hardy Limeback adapted from http://fluoridealert.orgldental-fluorosis.htm )

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The benefits of reduced dental caries and the risk for enamel fluorosis are linked. Early studies

that examined the cause of "mottled enamel" (now called moderate to severe enamel fluorosis)

led to the unexpected discovery that fluoride in community drinking water inhibits dental

caries (Dean 1938). Historically, a low prevalence of the milder forms of enamel fluorosis has

been accepted as a reasonable and minor consequence balanced against the substantial

protection from dental caries from drinking water containing an optimal concentration of

fluoride, either naturally occurring or through adjustment (Dean 1942).

2.S.1.1 INDICES OF DENTAL FLUOROSIS

Several indices have been used to describe the clinical appearance of dental fluorosis. The four

major ones used are:

• Dean's index (developed between 1934 and 1942)

• Thylstrup and Fejerskov Index ( 1978)

• Tooth Surfuce Index of Fluorosis (Horowitz et at 1984)

• Fluorosis Risk Index (pendrys 1990)

Other indices which have sometimes been used are Smith's Index, Developmental Defects of

Enamel (ODE) and Clarkson and O'Mullane Index. These indices are not very popular since

they are more examiner subjective than the above mentioned indices.

The continued use of Dean's index for more than fifty years is a testament to its simplicity

and utility. It classifies individuals into 5 categories, depending on the degree of enamel

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alteration, and which was based on the identification of the 2 most severely affected teeth,

giving ordinal numbers as the severity of the enamel alteration increased.

The index has been criticised because it presupposes the condition and because criteria are

unclear for some categories or lack sensitivity, particularly for severe fluorosis. Another

criticism is related to its use of either the person or the community as the unit of measurement.

While basing the person- level score on the most severely affected teeth serves the purpose of

measuring the maximum dental effects of fluoride dental exposure, important in determining

the safe level of exposure to fluoride from drinking water, it is not useful in those instances

where the type of tooth or surface affected is important. Three problems can arise from use of

this person score:

• Aggregation across surfaces or teeth may prevent adequate discrimination among

individuals, particularly at high fluoride levels where all subjects may have pitting

in some teeth.

• A person- level score may misclassify an individual if aesthetic considerations are

more important than biological ones, since the most affected teeth tend to be the

posterior ones which have less cosmetic importance than anterior teeth.

• The person-score does not permit determinations of possible changes in the level

of fluoride exposure during tooth development.

Since the Community Fluorosis Index (CFJ) is an average, it provides little information about

the variation within a popUlation, particularly if measures of variance are not provided, which

is the usual case when reporting CFI values. Also, since it is a weighted average, individual

scores may not correlate well with the community score and thus may misrepresent the dose­

response relationship between fluoride and fluorosis since a large number of questionable

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ratings can produce a CFI of the same magnitude as that in a population with fewer

questionables but with higher scores (Fejerskov et aI1988).

Another major criticism of Dean's Index concerns statistical manipulation and reporting,

primarily related to the use of the CFI. Since the classification system is based on an ordinal

scale, and the distribution of scores is usually not normal at some levels of fluoride exposure,

the mean is an inappropriate statistic. Further to this the weights assigned to each category are

arbitrary.

The Thylstrup and Fejerskov (TF) Index is appealing to clinicians and epidemiologists

since it corresponds closely to the histological changes that occur in dental fluorosis and to

enamel fluoride concentrations, thus having biological validity. A 10 point ordinal scale is

used to classify enamel changes associated with increasing fluoride exposure (ranging from 0

to 9 with a score of 0 being no fluorosis and a score of 9 being the worst type of dental

fluorosis). Most investigations have only used facial surfaces of teeth and this has become the

recommended procedure since 1988. This recommendation is based on the similarity of the

different surface scores on the same tooth, and on the difficulty of getting an accurate

assessment of fluorosis on occlusal surfaces because of the likelihood of scores being affected

by occlusal wear (Rozier 1994). The clinical and histological bases for the criteria used for

scoring fluorosis with this index have clarified by the way in which fluorosis is distributed

over the tooth surface in the case of continuous exposure to constant levels of fluoride during

tooth development, as well as the role of enamel loss in fluorosis. The approach used on

formulating scoring criteria has had the effect of reducing some of the subjectivity in scoring.

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The Tooth Surface Index of Fluorosis (TSIF) makes a useful contribution because it

provides clear diagnostic criteria and provides for an analysis based on aesthetic concerns. It

classifies individuals into 8 categories. In this index a value is given for each anterior tooth

surface not restored (buccal and lingual) and three values for posterior tooth surfaces (buccal,

lingual and occlusal). An advantage of TSIF is that it contains no questionable category, like

TFI, and thus a positive score is assigned to the first signs of fluorosis. TSIF scores 1-3 are

based on the area of the tooth surface affected, derived by visually coalescing all areas of

fluorosis and relating that area to the total visible enamel of a particular surface. The area of a

surface affected can provide a useful indication of severity when exposure to fluoride is

continuous during the development of the tooth. With interrupted fluoride exposure, however,

only a portion of the surface may be affected, and to various degrees depending on the level of

exposure. An inaccurate assessment of severity can be provided in those instances where

continuous and interrupted exposures result in identical scores based on surface area affected,

yet the severity of fluorosis differs.

Another point concerns the score of "4", given when staining is present in conjunction with

any of the three conditions indicative oflower scores. If one's primary interest is measuring the

aesthetic consequences of fluorosis, the index is probably an ordinal one. However, if the

index is being used solely as an indicator of the biological effects resulting from fluoride

exposure, the TSIF must be considered a nominal scale rather than an ordinal one according to

the purest defmition of scales. Since staining of any portion of the surface is given precedence

over the proportion of the surface affected with fluorosis, a score of "4" may be given when an

area equivalent to a TSIF score of "1" is present However, stain rarely occurs before a "mild"

level of fluorosis is reached according to Dean's Index, most likely corresponding to a score of

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"3" in the TSIF, and should not be of major concern if one wishes to treat the index scale as

ordinal.

The aesthetic orientation of this index is evident once again in the higher degrees of fluorosis,

where staining occurring in conjunction with discrete pitting is given a separate score. Finally,

a distinction between discrete pitting and more advanced confluent pitting is made, making the

index more sensitive than Dean's to higher degrees of fluorosis. Results obtained with the use

of this index are presented as various frequency distributions of surface scores or of the

maximum mouth score, either for all surfaces or for specific surfaces such as facial surfaces of

anterior teeth or occlusal surfaces of first molars.

With use of the TSIF, examiner reliability may be of more concern than with Dean's Index or

the modified TFI because of the larger number of assessments to be made (72 surfaces vs. the

usual maximum of 28 teeth or buccal surfaces in children). The added lingual surfaces are

more difficult to visualize than buccal surfaces, which also adds to the concern about examiner

reliability. The original publication documented examiner reliability for the two examiners

originally involved in the index. Intraexaminer agreement ranged from 0.66 to 0.83 for the two

examiners and for all teeth combined and for anterior teeth only. Interexaminer agreement as

measured by the kappa was 0.35 for all teeth, and 0.54 for anterior teeth, indicating some

difficulty in achieving an acceptable level of agreement for all teeth.

The TSIF has two major advantages over Dean's Index. First, criteria for scoring in the TSIF

are clearer, and consequently, subjectivity should be reduced in their application. The other

advantage derives from the scoring of surfaces rather than individual teeth. Surface scores

allow for analyses of fluorosis on the labial surfaces of maxillary anterior teeth (those surfaces

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of greatest aesthetic concern), and a more precise correlation of age of exposure with tooth

development, useful in analytical studies on risk factors and biological effects.

A further advantage may be the added sensitivity gained through the increased number of

scores compared with other indices. This sensitivity depends, of course, on the differences that

exist among the different surfaces, particularly between facial and lingual surfaces.

Further work needs to be done to determine the advantages of including all surfaces in an

examination. The added precision gained from such an exam must be weighed against a

possible small surface-to-surface variation for a given tooth, the higher probability of loss of

data on occlusal surfaces because of restorations, and the possibility of reduced examiner

consistency because of the inclusion of hard-to-see lingual surfaces.

The Fluorosis Risk Index appears to be particularly useful for analytical epidemiological

studies since it is designed to permit a more accurate identification of associations between

age- specific exposures to fluoride and the development of dental fluorosis (pendrys

1990).The validity of the fluorosis risk index utility has still to be determined since it has not

yet been widely used.

The unique feature of the FRI is that each tooth is divided into zones that correspond to the age

at which they begin development, and can be related to narrow age-bands of fluoride

exposure, such as a 12-month time period. Enamel surface zones that begin fonnation during

the first year of life (i.e., between birth and the :first birthday) and those that begin formation

between the third and sixth years of life (i.e., between the second and sixth birthdays) are

identified and scored separately. The buccal surface and the incisal edge/occlusal table of each

permanent tooth (excluding third molars) have been divided into four scoring zones: (I) the

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incisal edge/occlusal table, defined as the enamel surface within one millimetre of the incisal

edge of the tooth; (2) the incisaVocclusal third of the buccal surface; (3) the middle third of the

buccal surface; and (4) the cervical third of the buccal surface.

The portions of the enamel that begin fonnation during the first year of life are referred to as

Classification I enamel surface zones. The Classification II are enamel surface zones that

begin fonnation during the third through sixth years of life. The other category are the

unassigned enamel surface zones for which categorization is questionable, based on the

available literature on tooth development, or where their development occurred after 5 years of

age. Roughly 112 zones are scored, with 10 belonging to Classification I, 48 to Classification

II, and the remaining 54 to unassigned zones.

Each zone is scored as either negative for fluorosis, questionable for fluorosis, positive for

mild-to-moderate fluorosis, or positive for severe fluorosis. A surface zone is diagnosed as

being positive when 50010 or more of the area of a zone being scored is affected-according to

the authors, a severity level equivalent to the "mild" category in Dean's Index. The criterion for

this categorization in Dean's Index, however, is based on the proportion of the entire tooth that

is affected, not a surface or portion of a surface. Thus, the two classifications may not be

equivalent

Subjects are identified as cases or controls for each of the two surface zones based on the

distribution of scores within each. At least two surfaces of a particular zone must have scores

of 2 or 3 in order to be considered a case. In the analysis, risk factors are considered separately

for each classification.

The single use of this index has been reported by the authors (pendrys and Katz, 1989).

Examiner reliability studies during its initial use produced excellent results. The two

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examiners achieved interexarniner agreement, as measured by the kappa statistic, of 0.76 and

0.82 for Classification I and Classification II surface zones, respectively. Kappa statistics for

intra-examiner agreement varied from 0.83 to 1.00 for the two types of surface classifications.

The strengths and weaknesses of the FRI should become more apparent with its use by other

investigators. The biological and analytical premises appear sound. While the ability exists to

collapse FRI values to yield prevalence data, the index was not designed for this purpose. In

most situations, the other three indices are better suited to provide strictly prevalence data. The

index is complex, both from a biological perspective and in its application. Acceptable levels

of examiner reliability may be difficult to establish due to this complexity. Further, results

cannot be compared with those of any of the established indices used in determining

prevalence. Therefore, the index cannot serve the dual purpose of providing prevalence

estimates as well as estimates of risk.

A primary premise of this index is that scores for the two age-related developmental zones are

independent The differential diagnosis of fluorosis required of this and other fluorosis indices

is usually based on an initial overall assessment of the dentition, since the intra-oral

distribution of fluorosis is useful in making a diagnosis. Before proceeding with specific tooth

calls, the examiner usually makes the initial assessment as to whether the subject is a case or

not This procedure cannot be followed with the FRI because of the likelihood of bias in

making determinations for the Classification I and II zones. Any existing bias in the

determinations between case, control or questionable in Classifications I and II could weaken

or even mask associations between exposure and outcomes. Case definition will affect the

identification of risk factors. The FRI is conservative in the definition of surface zones and in

the severity level chosen for a case. This conservative approach may create difficulties in

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identifying those factors that carry a small risk, or are widespread in the study population.

There is also a concern about the validity of assessments in Classification I, which are based

on only 10 surfaces, the incisal edges of mandibular incisors, maxillary incisors, and occlusal

surfaces of first molars. Incisal edges of anterior teeth are more likely to demonstrate clinical

signs of fluorosis than many other surfaces, probably because of a smaller amount of dentin,

their increased translucency, and the tendency for these surfaces to be drier than others.

Further, the occlusal surfaces of first molars are those surfaces most likely to be excluded

because of restorations, and presumably dental sealants. Not surprisingly, over 60% of

Classification I cases involved the incisal edges of anterior teeth (Rozier 1994).

The acceptance of these fluorosis indices rests largely on the ability of the examiner to

distinguish fluoride- induced changes in the enamel from those that are not fluoride- induced

(Table 6).

Opaque white lines or clouds- chalky appearance

Always on homologous teeth

Usually centred in smooth surface

Round or oval

surfaces

Table 6: Comparison of characteristics of Dental Fluorosis and NOB- Fluoride Enamel Opacities

There is little epidemiological evidence that opacities characteristic of dental fluorosis can be

caused by other factors (Rozier 1994). Trace elements other than fluoride have been

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investigated, yet only two human studies have shown such an association. Strontium (Curzon

and Spector, 1977) and Zinc (Butler et ai, 1985) have been associated with fluorosis-like

opacities, but these associations were found to be weak. For example in a study in 16 Texas

communities with fluoride levels in drinking water ranging from 0.2 to 3.3 ppm, water fluoride

was found to be accountable for 32 % of the variation in dental fluorosis, while various metals

accounted for 1% to 6% when considered singly (Segreto et ai, 1984). While there is no direct

evidence, the accuracy of fluorosis diagnosis may be as high as 95% for experienced

examiners who give proper attention to examination methods and the use of differential

diagnostic criteria.

2.8.1.2 AESTHETIC PERCEPTIONS OF FLUOROSIS

Knowledge of people's aesthetic perceptions of fluorosis is incomplete arid relatively few

studies have assessed it Some studies which have assessed people's aesthetic perceptions of

dental fluorosis, suggest that concerns may be greater than previously believed (Levy et al

2002). Other studies however, have observed that although the parents and children with teeth

affected by dental fluorosis perceive the presence of a change in tooth colour, associated with

fluorotic lesions, which was more obvious with TF scores of 2 or 3, this was not related to

unattractiveness of teeth. Children with a TF score of 1 were even more likely to perceive their

teeth as Attractive or Very attractive compared with children with a TF score of 0 or 2-3. The

latter two groups were similar in perceived attractiveness of their teeth (Loc and Spencer

2007). This finding was similar to that reported by Ellwood and O'Mullane (1995), Hawley et

al (1996) and Sigwjons et aI (2004). Hawley et al (1996) reported that TF scores of 1 or 2 even

enhanced the appearance of teeth as perceived by children. This phenomenon may be

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explained by the preference for more ''whitish'' tooth colour of deciduous teeth over

''yellowish'' colour of newly erupted permanent teeth during the mixed dentition period.

The risk of perceived aesthetic problems attributable to fluoridation must be weighed against

its lifetime benefits and the associated costs of alternative solutions (Griffm et at 2002). The

pennanent maxillary incisors are the teeth on which most aesthetic perceptions are based.

No studies about aesthetic perceptions of fluorosis have been carried out in the Maltese

islands.

2.8.1.3 TREATMENT OPTIONS FOR DENTAL FLUOROSIS

Treatment options for fluorosis vary and will depend in part on the severity of the fluorosis

and what the patient can afford (some of the treatments are very expensive). Some of the

more common treatments include:

Micro-abrasion: micro-abrasion involves finely sanding off the outer layer of the enamel.

It is a common approach when the fluorosis is mild. However, if the fluorosis is of a more

advanced severity, abrasion is not a ~ood idea as it can bring to the surface of the teeth

highly-porous enamel that will be prone to attrition.

Tooth Whitening: Tooth whitening does not remove the white lines caused by dental

fluorosis, but lightens the background, thus making the lines less noticeable.

Composite bonding: Composite bonding first involves lightly roughening the area of the

damaged enamel. After etching the enamel, a composite resin (with a colour matching your

teeth) is cured on to the exterior of the tooth.

Porcelain veneersllaminates: Made out of porcelain, veneers form a ceramic shell over the

labial surface of the tooth. The tooth needs to be prepared by removing a thickness of about

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2mm from enamel and dentine from the labial surface. The veneer will then be bonded to

the remaining tooth by means of an appropriate adhesive and will look like part of the

tooth. Veneers may need to be replaced after several years, however, which can become

quite expensive. They also require a certain amount of dental tissue loss in the preparation

of the tooth.

Porcelain crowns: Porcelain crowns cover the whole tooth and thus disguise the tooth

structure underneath. The tooth needs to be prepared by removing a thickness of about

2mm from enamel and dentine on all the tooth surfaces. The crown will then be constructed

in a dental laboratory, from an impression of the preparation, and bonded to the remaining

tooth by means of an appropriate adhesive. Crowns may need to be replaced after some

years, since their lifespan ranges from five to fifteen years, which can become quite

expensive. They also require a certain amount of dental tissue loss in the preparation of the

tooth for crown construction.

2.8.1.4 EVIDENCE OF DENTAL FLUOROSIS IN GOZO SO FAR

Evidence of dental fluorosis had been found among some school children in Gozo in 1964

(Vassallo, 1968). However no data were ever collected or presented during that period. The

first documented data on dental fluorosis was in 1986. Table 8 shows the distribution and

severity of dental fluorosis in 12 year old children in Malta and Gozo in 1986.

Gozo had the lower percentage of children who recorded nonnal (46.3%). There would appear

to be more fluoride in Gozo as the level of questionable fluorosis is highest, a value of 23.8%

as compared to 3.4% in Malta. However it was only in Malta that children had severe levels of

fluorosis. The percentage of children affected was however very low, 0.8010.

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Nonnal 62.4 46.3

Questionable 3.4 23.8

Very mild 15.9 15.0

Mild 14.6 8.8

Moderate 2.1 5.0

Severe 0.8 0.0

Table 8: Levels of dental fluorosis in 12 year old children in 1986 - percentage of persons affected (according to the modified Dean's index) (Sources: Moller, 1987; Department of Dentistry - Malta).

Fluorosis occurs during the first 6 years of life, when the teeth are developing. Thus, taking

into consideration the fluoride levels in the public water supplies from 1974 to 1980, which

are the first six years of life of the twelve year old children examined in 1986, one would

expect Gozitan children to have the highest levels of fluorosis. However, the values for Malta

are somewhat higher than expected according to the fluoride concentration in the drinking

water. This suggests that perhaps the clinical signs of dental fluorosis have been slightly

overscored or that non-fluoride opacities (Table 6) have not been excluded (Moller, 1987).

This may, however, also be due to the availability of fluoride from other sources.

Further data was then collected by Vassallo and Portelli in 2004 during the National Oral

Health Survey of the Maltese Islands. The data collected in this survey shows that 21 % of the

children examined in Malta and Gozo had staining of the upper incisor teeth attributable to

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fluorosis and 19 % of these children were aware of the stains. In Gozo 15 % (9) of the 12 year

old children examined (n=60 12 year olds) had marks attributable to fluorosis.

2.8.2 SKELETAL FLUOROSIS

In rare instances of excessive industrial exposure to fluorides or where natural waters contain

very high fluoride concentrations, particularly when consumed by undernourished or

malnourished population groups, crippling skeletal fluorosis, which is a bone disease

characterised by failure of the bone to mineralise properly, may occur. Fluoride intakes of 10-

25 mg, or more, daily for a period of 10-20 years are required (Hodge, 1979). The bones tend

to be weaker than normal bones and typically the bones of the legs become deformed due to

weight bearing. This disease is characterized by severe osteosclerosis, fresh areas of

osteoporosis, exostoses and calcification of certain ligaments, tendons and muscle insertions

which may result in disability. Skeletal fluorosis is a widespread problem in several

developing countries such as India and Pakistan due to high fluoride exposures mainly from

high fluoride levels in drinking water (up to 18 ppm in 15 Indian states), and hot climates

(therefore increased water consumption).

A number of studies have investigated the fluoride exposure and hip fracture risk. Results vary

with some studies showing a slight protective effect, others a slight increase in fracture rates

and others finding no effect. Mc Donagh et al (2000) conducted a meta analysis of several

studies on bone fracture and water fluoridation and no effects were found except in studies of

10 years or longer, in which case a protective effect of water fluoridation on :fracture risk was

shown.

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2.8.3 OTHER EFFECTS

A number of other toxic effects and specific health problems have been suggested including

cancer, renal disease, allergies, teratogenicity, allergy and immunological effects, effects on

reproduction, birth defects and other biochemical effects.

"It is a toxic effect and a cosmetic effict. These are not mutually exclusive. It's toxic and it's cosmetic. " - Dr. Arvid Carlsson, Nobel Prize Laureate in MedicinelPhysiology (2000).

There has been a lot of campaigning internationally but especially in the United States of

America against fluoridation.

"Like bones, a child's teeth are alive and growing. Fluorosis is the result of fluoride rearranging the crystalline structure of a tooth's enamel as it is still growing. It is evidence of fluoride's potency and ability to cause physiologic changes within the body, and raises concerns about similar damage that may be occurring in the bones." - Environmental Working Group, 2006.

Special importance is being given to Dental Fluorosis, since it is a systemic effect, with a lot of

theories as to other possible systemic damage caused by fluoride ingested in water.

"A linear correlation between the Dean index of dental fluorosis and the frequency of bone fractures was observed among both children and adults." - Alarcon-Herrera MT, et al. (2001).

These claims to systemic damage have as yet not been adequately supported by enough

evidence from studies and are more theoretical. They are being used by several organisations

who are lobbying in favour of cessation of water fluoridation and against further water

fluoridation. However, considerable evidence has been presented, indicating that fluoride

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exposure does not represent any carcinogenic or teratogenic hazard, and no effects on

mortality patterns have been detected. Numerous searching reviews of the safety of

fluoridation have been unable to find any adequate grounds for these allegations of harm. The

claim that fluoride played any role in the other problems has never been substantiated (WHO,

2004).

2.9 CONCLUSION

There is no doubt that the use of fluoride decreases dental caries. On the other hand it is clear

that the ingestion of too much fluoride can result in varying degrees of fluorosis. Thus in

practice, the administration should strike a beneficial balance between the two situations.

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CHAPTER 3 METHODOLOGY

3.1 GENERAL DESIGN OF THE STUDY

This chapter presents and discusses the methods used to carry out the study. The project is an

observational study based on three main sources of infonnation:

A literature review;

A clinical examination of evidence of fluorosis in 5 year old and 12 year old Gozitan school

children;

A question about the aesthetic perception of fluorosis asked to the 12 year old school children.

After approval for the study protocol was given by the Department of Public Health at the

Faculty of Medicine and Surgery of the University of Malta, a request for pennission to carry

out this study was submitted to the Department of Planning and Development of the Education

Division (Appendix 2). Pennission was granted on the condition that approval for the dental

examination is given by parents.

An application for pennission to carry out the study protocol was then submitted to the

Research Ethics Committee. (Appendix 3)

All schools in Malta and Gozo send out consent fonns at the beginning of each scholastic year,

for parents to give signed approval for dental examinations to be carried out for their children

at the school they attend. The children whose parents do not consent to dental examinations

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are not sent for examinations when dental surgeons or dental hygienists attend to perfonn

screening procedures in the school. In the case of this study, the same conditions applied.

3.2 LITERATURE REVIEW

First, a literature review was undertaken. A critical review of the relevant literature was carried

out in order to provide the scientific basis for the study.

The relevant infonnation was obtained from official and professional organizations, recent

textbooks on preventive dentistry and fluorides, reports from both workshops and meetings,

reviews from different authors and relevant articles and surveys.

The selection of the index used for this study came about after looking at the available tools

reviewed in the literature review. It was decided that the best tool to reach the objectives of

this study was the TF Index since it is sensitive, has high intra examiner reliability, has

reduced examiner subjectivity and does not require a complex examination and could thus be

carried out in schools.

3.3 EXAMINER TRAINING

The examiner underwent training on physical characteristics of fluorosis from the data

gathered in the literature review, photos found on books and on databases of pictures on the

internet, and examination of the details of the TF Index.

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3.4 STUDY POPULATION

The study populations of 5 year old and 12 year old school children were chosen since these

are the ages at which clinical surveys for oral health are being carried out. This was done so

that comparisons can be made between the results and also to maintain consistency in the age

of reporting. The study was carried out in all the public schools and all the church schools in

Gozo. All the children who had a positively filled consent form and who were present at

school on the day were examined. Other information gathered on examination includes:

• Locality in which the child lives.

• History of relocation up to when child was 6 years of age.

• In the case of the twelve year old school children only, a question regarding stains on

their upper anterior teeth which could not be removed with a toothbrush was asked.

Inclusion Criteria:

• Consent for dental examination from parents.

• Children must be either 5 or 12 years old.

• Children must have lived in Gozo from birth until a minimum of 6 years of age.

• 5 year old children must have a minimum of 6 anterior teeth present which should

be unrestored and should not have smooth surface carious lesions.

• 12 year old children must have a minimum of 6 anterior teeth present which should

be unrestored and should not have smooth surface carious lesions

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3.5 DATA COLLECTION

3.5.1 FLUOROSIS DATA

A clinical examination of 5 year old and 12 year old Gozitan school children was carried out

using intense light and tongue depressors. The observations were then recorded using the TF

Index (Table 7) which describes the clinical appearance of dental fluorosis. Infonnation as to

the locality where the child currently lives in the case of 5 yr olds and where child lived up to

6 years of age in the case of the 12 year old children was obtained and recorded. The scores

and answers were recorded by a dental hygienist who was acting as a clerical assistant.

pronounced lines of opacity confluence of adjacent lines. Occlusal sUrfaces: Scattered areas of opacity <2 mm in diameter and pronounced opacity of cuspal

entire surface exhibits marked opacity or appears exposed to attrition appear less affected. Occlusal surfaces: Entire sUrface exhibits marked opacity. Attrition is often pronounced shortly after

Smooth surfaces and occlusal sUrfaces: Entire surface displays marked opacity with focal loss of outermost enamel (pits) <2 mm in diameter.

Smooth surfaces: Pits are regularly arranged in horizontal bands <2 mm in vertical extension. Occlusal sUrfaces: Confluent areas <3 mm in diameter exhibit loss of enamel. Marked attrition.

.• 'c;y' •••. '71 Smooth surfaces: Loss of outermost enamel in irregular areas involving <112 of entire sUrface. Occlusal surfaces: Changes in the morphology caused by merging pits and marked attrition.

Smooth and occlusal surfaces: Loss of outermost enamel involving> 112 of surface.

Smooth and occlusal surfaces: Loss of main part of enamel with change in anatomic appearance of surface. Cervical rim of almost unaffected enamel is often noted

Table 7: Clinical Criteria and Scoring for the TF IndeL (fhylstrup- Fejerskov 1978)

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3.5.2 INTRAEXAMINER RELIABILITY

Intraexaminer reliability was tested. This was done by having the clerking assistant call back

one child, from every group of twenty children seen. The child was then re- examined and re­

scored using the TF Index. The scores were recorded and the Weighted Kappa was then

calculated.

3.5.3 AESTHETIC AWARENESS DATA

The 12 year old school children were asked the question "Are you aware of any marks on

your upper front teeth which will not brush oft'?" translated in Maltese to ''Taf jekk

ghandek xi marki fuq snienek ta' fuq ta' quddiem Ii ma jmorrux anke jekk toghrokhom?"

Answers were recorded and divided into the categories: Yes, No and Don't Know.

3.5.4 PUBLIC WATER SUPPLIES

A request for data was sent to the Institute of Water Technology, responsible for the routine

check monitoring programme and the Audit Monitoring Programme (set up to meet the

requirements of Legal Notice 23 of 2004 and 116 of 2004, Food Act 2002), at the Water

Services Corporation to provide information on the fluoride levels in the water supplies of

Gozo. Data on the amount of water coming from the reverse osmosis plants were also

requested.

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3.6 ANALYSIS AND PRESENTATION OF DATA

The data collected were then entered onto a personal computer.

Statistical analysis was carried out using the SPSS package. Non- parametric tests such as

Kruskal- Wallace test, Mann- Whitney test and Speannan's Correlation were used for

statistical analysis.

The results were presented in graphical and tabular form.

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CHAPTER 4 RESULTS

INTRODUCTION

This chapter presents the results of the study divided into three sections:

1. Data on incidence of fluorosis of the dental hard tissues in Gozitan school children.

This includes data for the deciduous dentition (obtained from the 5 year old school

children examined) and the permanent dentition (obtained from the 12 year old school

children examined) and the scores given according to the TF Index.

2. Data on aesthetic awareness of fluorosis for the 12 year old age group obtained from

the replies to the question "Are you aware of any marks on your upper front teeth

which will not brush oft'?"

3. Fluoride availability. This includes the fluoride levels in the public water supplies in

the sixteen different localities in Gozo.

4.1 DENTAL FLUOROSIS

4.1.1 RESULTS OBTAINED FOR FLUOROSIS IN 5 YEAR OLD GOZITAN

SCHOOL CHILDREN.

270 five- year old school children were examined for the purpose of this study, out of which

138 were males and 132 were females. 97 (36%) of these children attend church schools and

173 (64%) attend public schools. 28 five year old children were absent or did not have signed

consent forms on the day of the examination (15 females and 13 males). 2 males were not

included in the study as they did not fulfill all the inclusion criteria for this study.

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In the 5 year age group the percentage of children affected by fluorosis is very low (Figure 9).

Only 8 children (1.8%) had a score on the TF Index, and that score was 1 which is barely

visible to the naked untrained eye (Figure 5). There was no statistically significant difference

between children attending public or church schools (p value 0.072) and between females and

males (p value 0.642) using the Mann Whitney test to analyse the data in both cases. A Non-

parametric test was used since the group analysed (positive for fluorosis) contains a small

number of children.

Zebbug & Marsalfom

Xewkija

Xaghra

Sannat

San Lawrenz

Rabat

Qala

Nadur

Munxar & Xlendi

Kercem

Ghasri

Gharb

Ghajnsielem

Fontana

-\a

'-

~ I

_0

• P

I

o

I

I

10 20 30 40 50

Number of children

Figure 9: TF scores in 5 year old Gozitan school children.

• TF Score 1

o TF Score 0

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o

4.1.2 RESULTS OBTAINED FOR FLUOROSIS IN 12 YEAR OLD

GOZITAN SCHOOL CHILDREN.

348 twelve- year old school children were examined for the purpose of this study, out of which

177 were males and 171 were females. 80 (23%) of these children attend church schools, 97

(27.9%) attend public secondary schools and 171 (49.1 %) attend public junior lyceum schools.

26 twelve year old children were absent or did not have signed consent forms on the day of the

examination (19 females and 7 males). 5 males and 1 female were not included in the study

due to not fulfilling all the inclusion criteria for this study.

Zebbug & Marsalfum

Xewkija

Xagbra

Sannat

San Lawrenz

Rabat

QaJa

Nadur

Munxar & X1endi

Kercem

Ghasri

Gharb

Ghajnsie1em

Fontana

~ I i;I

b e p

L 8.

i;J.

F===

'" F>.

~l o 10

!

20 30 40

Number of Children

50 60

OTF Score 5

. TF Score 4

o TF Score 3

OTF Score 2

• III TF Score 1

OTF Score 0

Figure 10: TF scores in 12 year old Gozitan school children.

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13.8% (48) of the children had a TF score of I or more. 23 (6.6%) 12 year old children had

a TF score of I, 11 (3.16%) had a TF score of 2, 10 (2.87%) had a TF score of3, 3 (0.86%)

had a TF score of 4 andl (0.29%) had a TF score of 5 (Figure 10).

There was no statistically significant difference between sexes (p value 0.642) or type of

school (p value 0.072) when using the Mann Whitney test. As in the 5 year olds, a Non-

parametric test was used since the group analysed (positive for fluorosis) contains a small

number of children.

Using the Kruskal Wallis test, the mean TF scores were analysed by locality. A p value of

0.005 resulted making the differences in fluorosis between localities statistically significant.

The 95% confidence intervals of the means were then calculated and are represented in Figure

II below. The upper and lower centiles represent the maximum and minimum values of the

confidence intervals respectively.

1.2'1-----------------------------

! o o

'"

0.8

l!: 06 c .. • :E

0.4

0.2

o

I

I 1 I

I : I

I

I r-

I

il ~ I ~ r 1 r ~ r r -,

J 0 I . 1

Locality

Figure 11: Mean TF scores with their confidence intervals by locality.

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This bar chart shows that the mean TF score of Xaghra, which is the locality with the

highest fluorosis, is significantly higher than that of all the other localities apart from

neighbouring Zebbug (including Marsalforn) and Gharb.

Figure 12 shows the Mean TF scores of localities plotted on a Gozo map. The localities of

Xaghra, Zebbug and Marsalforn and Gharb on the North West of the Island are the worst

affected area with Qala in the East following closely behind. This pattern does not follow

the same pattern as the fluoride levels in water (Table 9).

• R.. ... B:\T 01C10Rl. ... )

.xn\1aJA

)I~&:'! TF xor~ .~ - .S

• GH. ... ,r..;SIllOI

Figure 12: Map of Gozo showing Mean TF scores by Locality.

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4.1.3 RESULTS OBTAINED FOR INTRAEXAMINER RELIABILITY.

31 children were re-examined to check intraexaminer reliability. The examiner was blind to

the first TF score obtained by the previous examination of the child. The first reading and

the second reading matched in 100 % of cases, thus giving a Weighted Kappa Value of 1.

4.2 AESTHETIC AWARENESS

Aesthetic awareness of fluorosis was investigated by asking the 348 Gozitan 12 year old

school children about awareness of marks on their upper front teeth which would not brush

off. 38 (11%) of the 12 year old children were aware of marks on their upper incisors which

would not brush off, whilst 289 (83%) were not aware of any such marks on their upper

incisor teeth. 21 (6%) of the 12 year old children did not know if they had any marks on

their front teeth which do not brush off.

From the 38 (11%) children who were aware of marks on their upper incisor teeth only 3

(8%) had marks which could be attributed to fluorosis, with a TF score of 2, 3 and 4

respectively; the others had other enamel opacities which are not classifiable as fluorosis. This

means that only 0.86% of all the 12 year old children examined were aware of marks on their

front teeth which were attributable to fluorosis.

4.3 FLUORIDE AVAILABILITY

Natural fluoride in tap water, which is the most readily available source of fluoride for the

population in Gozo, for the 14 Gozo localities, is shown in Table 9. The fluoride average

for Gozo is decreasing with time, especially since the introduction of the Collection scheme

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in 2005, which has included polished water into the mixture supplied to all Gozitan

households. The Fluoride levels in the water supply have dropped from 2.5ppm in 1994 to a

mean of 0.94ppm in 2000 and a mean of 0.44ppm in 2006 with an unequal distribution of

fluoride levels between the different localities.

Enamel mineralisation happens mainly at the age of 6 months to 6 years, thus the years

when the fluoride levels in tap water could have systemically affected the 12 year old

Gozitan school children to produce the levels of fluorosis which were found on clinical

examination in 2006, are the years between 1994 and 2000. The correlation between mean

fluoride concentration between 1994 and 2000 and TF scores by locality was analysed

(Figure 13). Spearman's correlation analysis of the data shows no correlation between the

two factors with a resulting p value of 0.68.

0.8

• 0.7 -'

0.6

• 0.5

• ., 0.3

0.2 • • • .. .. 0.1 -A

0~1----------~--------+-~----------~:~,----------~,.~--------~ o 0.5 1.5 2 2.5

Fluoride concentration (ppm)

Figure 13: Graph showing correlation between fluoride concentration and TF scores by locality.

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-.:t r-

= ~ ~ s! III QC QC g: ~ ~ = = M a ~ ~

III III

~ \C c:I'I c:I'I .

.Q.. = g g = ~ "It ~ c:I'I .... .= =: = . . . u = = =

GI c:I'I t> . ... !::: GI M! M M M = ~ .... . . .= .c ~ .c

~ Q r/.l . M . M M

M

~ GI • ~ !::: ~ ~ ~

I .c

I

~ .c ~ .c .c -= ~ Q.. ~ r: r: .; ....

= - ~ r: = r: fIl

.; = .; ~ 1: ~ 1 -< = GI

~ ~ • I I I I I I ~ ~

0 ~ ~ .c = ..L = ..L = = = ~ = ~ ~ ~ .; ~ .; ~ ~ .; -<

0.90 I 1.63 I 1.33 I 1.57 I 1.20 I 0.94 I 0.86 I 0.75 I 1.20 I 1.03 I 1.41 I 1.04

Table 9: Fluoride levels in water by locality in Gozo in ppm

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CHAPTERS DISCUSSION AND CONCLUSIONS

This study has focused on the impact that the prevalence of dental fluorosis has on the

public health in Gozo. It has also focused on the effect that the fluoride content of the public

water supplies in Gozo has had on the level of dental fluorosis in 5 year old and 12 year old

school children, and the aesthetic perceptions of dental fluorosis by the 12 year old school

children. A review of the literature was undertaken to explore the legal and ideal

concentrations of fluoride that should provide significant prevention of dental caries without

causing unaesthetic dental fluorosis.

Although fluorosis is not life threatening, it can cause unnecessary distress to a minority of

the population in its more severe forms, and it is also an economic burden to those citizens

who are affected where aesthetic problems are associated with the more severe forms of

dental fluorosis where reparative restorative treatment is required. The fact that funds

available for health programmes are always limited make it important to determine the types

of programmes that will be the most effective in improving oral health conditions without

any negative consequence, within the limitations of available resources.

5.1 FULFILLMENT OF THE STUDY OBJECTIVES

This section serves to evaluate the fulfilment of the objectives that the study set out to

address.

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5.1.1 DETERMINATION OF PREVALENCE OF DENTAL FLUOROSIS

IN THE DECIDUOUS DENTmON.

The prevalence of fluorosis in the deciduous dentition has previously never been

determined. The prevalence of dental fluorosis in the deciduous dentition is currently

negligible and this made statistical analysis of the fluorosis data by locality impossible to

carry out for the 5 year olds since the numbers were too small. Ideally these children

should be followed up for fluorosis when they are twelve years old (in 2013) so that

comparisons and analysis of correlation can be carried out between fluorosis in deciduous

and permanent dentition of these same children.

5.1.2 HOW LARGE A PUBLIC HEALTH PROBLEM IS DENTAL

FLUOROSIS IN GOZO CURRENTLY?

This study shows that at present, fluorosis is not a public health problem in Gozo. In

particular, for the twelve year old cohort studied, absence or presence of fluorosis will

remain the same throughout their life, since fluorosis develops between 0 and 6 years of life,

and thus will be valid for the cohort's lifetime.

In the five year old cohort studied, one can only state that negligible fluorosis was recorded

in the deciduous dentition and nothing can be inferred from this result to their permanent

dentition.

Taking into consideration the decreased levels of fluoride in water since the introduction of

the collection scheme, one would postulate that the levels of dental fluorosis in children in

Gozo should decrease even further, thus further decreasing the threat of fluorosis being a

possible public health problem.

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.J

5.1.3 MONITORING TRENDS OF DENTAL FLUOROSIS

This study serves as a comparison with the available data. When comparing to the data from

1987, one can see a decrease in the levels of dental fluorosis. The fluoride levels in the

potable water supplied to Gozitan households between 1975 and 1981 (when the 12 year

old children examined in 1986 were 0 to 6 years old) are not available. The water supplied

was unpolished ground water, which one can assume was very similar to the kind of water

available between 1994 and 2000 which was studied in this study.

Actual numbers of imports of fluoridated vehicles such as fluoride toothpastes and

mouthwashes are not available for 1975 to 1981, but they would most probably be less than

what was between 1994 and 2000. Therefore this suggests that perhaps in the report

published by Moeller in 1987 the clinical signs of dental fluorosis might have been slightly

overscored or that non-fluoride opacities (fable 6) had not been excluded.

Since dental fluorosis occurs during the first 6 years of life, when the teeth are developing,

taking into consideration the fluoride levels in the public water supplies from 1994 to 2000

(in the case of the twelve year olds) which vary, according to locality, between 0.88ppm and

2.03ppm, one should expect quite a high prevalence of dental fluorosis with high scores in

certain localities where fluoride concentrations exceed 1 ppm. This is in fact not the case as

the results obtained show that the prevalence of fluorosis is 13.8 % with only 4.2 % of the

population having a TF score between 3 and 5 which is considered mild to moderate and no

TF scores higher than 5 were recorded. In the National Oral Health Survey of the Maltese

Islands in 2004, Portelli and Vassallo examined 60 Gozitan children and found 9 of them

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(15%) with signs on their upper central incisors attributable to fluorosis. The results

obtained in this study are quite similar to this value. The National Oral Health Survey did

not give scores of fluorosis to the children examined so scores could not be compared.

The results of this study also show no correlation between the fluorosis prevalence and the

fluoride levels when analysed by locality. This indicates that the fluoride concentration in

drinking water is not the solitary source from which dental fluorosis is developing and

that other fluoride vehicles are affecting the children with systemic absorption of high

enough concentrations of fluoride, which in addition to the fluoride concentrations in

potable water, cause fluorosis.

This causes questions to arise as to what other fluoride containing vehicle is causing enough

systemic absorption of fluoride in the fIrst six years of life of the Gozitan children to be

causing the level of dental fluorosis found in this investigation and why is tap water not

directly correlated?

There are probably two main reasons for this fInding:

• Increased use of bottled water rather than tap water.

From the National Oral Health Survey of the Maltese Islands (2004),400/0 of the twelve

year old respondents drank only water on a daily basis and 16% drank only water and

something else. 24 % of these children drank bottled water, 31 % drank fIltered tap water

and 45 % drank unfIltered tap water. In the case of the questionnaire sent to parents ofthe

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5 year old children in the Oral health survey, 55 % of households used bottled water, 6 %

used unfiltered tap water and 35 % used tap water only for making tea or coffee.

• Increased use of fluoridated dentifrices

Fluoride is readily available in the form of toothpastes. A standard tube of toothpaste

contains about 125 grams of toothpaste (generally containing 1500 ppm fluoride). In

Malta 135,523 kg (approximately 1,084, 100 tubes) oftoothpastes were imported in 2006

(NSO) which is a substantial increase from the 458,655 tubes of toothpastes imported in

1995. It is important to note that the data refers to dentifrices in general and not specifically

fluoridated toothpastes.

From the National Oral Health Survey of the Maltese Islands carried out by Portelli and

Vassallo in 2004, only 20% of people use the recommended pea sized amount of

toothpaste when brushing their teeth with 73% using more than the recommended amount

(Figure 14).

Parents should be advised not to use toothpaste when brushing their children's teeth until the

age of2 years. Prior to this age, parents should brush their children's teeth with a toothbrush

and tap water. Professional advice on the use of fluoride toothpaste should be sought where

a child below 2 years of age is considered to be at high risk of developing dental decay.

Parents should also supervise children aged 2 to 7 years when brushing their teeth and

should ensure that only a small pea sized amount of fluoride toothpaste is used and that

swallowing of the paste is avoided.

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42%

o NO BRUSHING

BRUSHING NO TOOTHPASTE

o PEA SIZED AMOUNT

o HALF BRUSH

• FULL BRUSH

o OVERFLOWING BRUSH

Figure 14: Breakdown of response as to use of toothpaste from the National Oral Health Survey of the Maltese Islands carried out by Portelli and Vassallo in 2004.

Currently, the localities affected most by dental fluorosis are Xaghra, Zebbug and

Marsalfom, Qala and Gharb. Since it has been determined in the results that the levels of

fluoride in the water supply and the levels of dental fluorosis are not correlated, more

investigations need to be carried out into why and what is causing these localities to have a

higher prevalence of dental fluorosis than other Gozo localities.

5.1.3.1 HOW Wll..L THE NEW WATER SUPPLY SYSTEM AFFECT

ORAL HEALTH IN GOZO IN THE FUTURE?

The latest reports on the fluoride content of the public water supply in Gozo, show that the

mean level of fluoride is below 0.5 ppm. This has dropped significantly from the mean

levels of fluoride in the 90s and the early years of this decade where there was a yearly

variability of fluoride levels between 0.75 and 2.5 ppm.

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The substantial reduction in the fluoride concentration in the tap water is a direct

consequence of the increased production of, nearly fluoride free, reverse osmosis water.

Also, ground water may show variations in the fluoride content depending on the presence

of fluoride containing fonnations at different depths. The ever growing population, the

industrial development, agricultural demands, together with the expansion of the tourist

trade and the increasing standards of hygiene, are putting more strain on the water supplies.

Thus desalinated or polished water is likely to contribute more water to the water supply in

future.

The data from this study will serve for comparisons to be made in the future when studies to

assess the effect of the newly introduced polished water on dental fluorosis are carried out.

These studies should ideally be carried out in 2010, to assess possible changes in fluorosis in

deciduous dentition (5 year olds) 5 years after the introduction of the collection scheme and

get an intennediate reading for the twelve year olds, and in 2017 to assess possible changes

to fluorosis levels in the pennanent dentition due to the collection scheme. Gozo can now be

subdivided into water supply zones for fluorosis comparisons to be done between supply

zones since the fluoride levels tend to vary between different water zones.

5.1.3.2 IMPACT ON DENTAL CARIES

The differences in the fluoride content of the public water supplies are reflected in the caries

levels of the Malta and Gozo. Overall, the data available shows that the caries level in the

Maltese Islands is low. The incidence of dental caries being lower among the Gozitan school

children, than it is among their Maltese counterparts (Figure 14). This implies the possibility

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that the incidence of dental caries is lower in the Gozitan school children due to the

fluoridated water supply, which Malta currently lacks.

This situation will probably also change, since the current fluoride level in tap water (mean

of 0.5 ppm for Gozo) is insufficient in maintaining oral health. Therefore, there is a good

probability that in time the DMF-T for Gozo will increase and there will be negligible

difference between the trends of Malta and Gozo (2004 trend shown in Figure 15).

4,-----------------------------------------------,

3.5

3

2

1.5

1

--amf! '='IF 010. __ DI.IFT 12 yr olos

Figure 15: shows DMF-T in 5 and 12 year olds (from Portelli and Vassallo 2004) against Fluoride in water in the Maltese Islands. (Sorted by Electoral Districts; Gozo is

District 13)

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5.1.4 DETERMINATION OF AESTHETIC AWARENESS OF

CHANGES ASSOCIATED WITH DENTAL FLUOROSIS IN

THE 12 YEAR OLD CHILDREN.

The prevalence of fluorosis in the pennanent dentition of twelve year old school children

was also detennined. The whole population was investigated rather than a sample so that

a clearer picture as to the real situation could be obtained. The twelve year olds were

asked a question relating to the aesthetic awareness of changes associated with dental

fluorosis. Only 14 cases of dental fluorosis which scored 3 or more on the TFI index were

found. The level of3 of the TFI scores is considered equivalent to a Dean's Classification

of "mild" and is judged to be a level which may cause aesthetic concern to the patient

(Mc Donagh et al 2000). Out of these 14 cases only 3 children were aware of any stains on

their upper central incisors. The children seem to be greatly unaware of any unaesthetic

changes associated with dental fluorosis and seem to be much more aware of non­

fluorotic enamel opacities.

The results obtained from this study show that there is very little fluorosis which can

cause an aesthetic concern to the children in Gozo today.

This cements the conclusion that at this point in time, fluorosis does not seem to be a

public health problem in Gozo, unlike the result that was obtained in the path finder

survey carried out by Moeller in 1986 and published in 1987.

This also correlates with Dean's Findings in 1942, where fluoride at a concentration of 1

ppm in drinking water caused only 'sporadic instances of the mildest fonns of dental

fluorosis of no practical aesthetic significance'.

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5.2 LIMITATIONS OF THE STUDY

This study has a number of limitations.

• Since a percentage (9.4%) of the 5 year old students were absent there could be a

slight variation in results in the true population.

• Large confidence Intervals in the results were inevitable in this study since such

small numbers of positive fluorosis cases were available.

• Ideally any clinical examination should be carried out in a dental clinic using

compressed air so that the teeth are dry and all defects are clearly visible. This could

not be done in this study since it would be difficult to carry out logistically. For the

examination to be carried out in a dental clinic all the students would have had to be

invited to attend and that would have meant a higher percentage of absenteeism. If

this study had been carried out in a dental clinic, there could possibly be an

increased detection of TF Scores 1 and 2, but would not influence detection of

scores higher than TF 2 and thus would only influence the prevalence but not the

severity of fluorosis.

• The TF Index, although having biological validity and being easy to use, has some

inherent limitations. The distinction between certain scores is quite SUbjective. This

is seen mostly between TF Score 4 and TF Score 5, with both categories being

defmed by marked opacity on the entire smooth surface with some additional

features which are slightly different. This may lead to a level of subjectivity in the

judgement of the examiner in determining how to score the individual being

assessed. In the results obtained in the study there were only 3 children who

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scored a TF score of 4 and only 1 child who scored a TF of 5, thus this should not

greatly affect the outcome of the study. Also, TF Scores 3 to 5 fall in the category

of Mild to Moderate Fluorosis so any interchangeability between the two scores

mentioned should not greatly affect any result.

Another limitation of the TF 'index is that it is not a continuous scale, but an ordinal

scale and, therefore, the scores should be considered only as arbitrary points along

a continuum of change. A preferred method would be to express the severity of

dental fluorosis in a continuous scale by showing the position of different

observations relative to each other and the extent to which one observation differs

from another. These properties are extremely important when the correlation

between two factors is studied, as well as when evaluating the cause-and-effect

relationship between two variables. Continuous scales for assessing the severity

of dental fluorosis are being created and validated but as yet have not been used in

clinical studies.

The conclusions that can be drawn from this study are that:

• The level of dental fluorosis in Gozo is negligible in the deciduous dentition of

the 5 year olds. Dental fluorosis is low in the permanent dentition of the 12 year

olds and the majority of the fluorosis present is of a mild form. Thus, currently,

dental fluorosis is not a public health problem in Gozo, unlike what was reported

in the path finder survey by Moller in 1987.

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• The 12 year old children are not aware of the aesthetic changes on their central

incisors associated with dental fluorosis.

• There is a significant difference in the prevalence of dental fluorosis in permanent

dentition when analysed by locality.

• The systemic source of dental fluorosis which is present in Gozo is not singularly

tap water, as was previously assumed, but rather a mixture of the tap water and

the use of other fluoride containing vehicles such as fluoride toothpastes,

mouthwashes and supplements used at an early age when a child is susceptible to

dental fluorosis whilst enamel mineralisation is taking place.

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CHAPTER 6 RECOMMENDATIONS

Since from this study it is concluded that fluorosis in Gozo is currently not a public health

problem, the following recommendations can be suggested:

• Against a background of exposure to multiple sources of fluoride and changes in

the rates of dental decay, dental fluorosis and fluoride levels in water, it would be

appropriate to define the optimal level of fluoride in the potable water in Gozo on

both a population and individual level, taking account of these altered

circumstances. This would enable a multi sectoral approach to be adopted by the

Government and ideally artificially fluoridate the Maltese Islands' water supply.

This has now become possible due to the new less complicated network of water

supply zones and would be possible if more liaising is done with the Water Services

Corporation. However, since there would surely be some kind of opposition to a

nationwide fluoridation campaign, the consumer's opinion should be sought by

means of a National Referendum prior to any such decisions being made.

Another alternative strategy would be for the government to work with

manufacturers to promote fluoride possibly through bottled water supplies,

especially since there is data to support that nearly one fourth of the population uses

bottled water as its source of drinking water. This would also take into account the

issues of personal choice since consumers can choose whether or not to buy

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fluoridated bottled water, a choice which is not possible if the potable water system

supplied to households is artificially fluoridated.

• Dental caries and dental fluorosis levels in Malta and in Gozo should be monitored

regularly so that all efforts can be made to reduce any inequalities associated with

them and also to prevent them from becoming oral health black spots. In fact the

Council of European Chief Dental Officers (CECDO) has emphasised the need for

identification of the oral health black spots and a reduction of the inequalities as

priorities for oral health.

Monitoring of dental caries in Gozo will become even more important since the

levels of fluoride in water have decreased, thus probably increasing susceptibility to

dental decay in the future population. Monitoring of dental fluorosis should be

continued both in the deciduous and the permanent dentition so that comparisons

between deciduous and permanent dentition of the same children can be done, and

also so that recent values are always available. These values can be used as a basis

for any Health Promotion campaigns on the correct use of fluoride which would be

required if the level of dental fluorosis is seen to be increasing. Up to date values of

both dental caries and dental fluorosis would be useful for monitoring of trends and

for taking decisions from a public health point of view such as whether it would be

beneficial or not to our population for water to be artificially fluoridated in every

locality on the Maltese Islands.

• Records of importation of toothpastes and other fluoride vehicles need to be

differentiated into fluoride containing and non-fluoride containing vehicles so that

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changes in both the importation and the use of these vehicles can be monitored. This

is important as it would give an overall view of the exposure to fluoride from

different sources and could be used to prevent an increase in the prevalence of dental

fluorosis. In particular, fluoridated dentifrice, fluoride mouthwash and fluoride

supplement sales should be monitored separately for the islands of Malta and Gozo.

• Further research on fluorosis should be carried out regularly with questionnaires sent

out to parents so as to determine tap water consumption, fluoride habits in

toothbrushing, and the possible use of other fluoride vehicles such as fluoride

supplements or fluoride mouthwashes. This could also become part of the

questionnaire used to carry out the National Health Survey, which is carried out by

the Department of Health Information every five years.

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)

APPENDIXl DEFINITIONS

Ground water is defined as any water occupying openings, cavities and spaces in rocks.

There are two main sources of such water:

* Juvenile water which rises from a deep magmatic source

* Meteoric water which is due to rainfall having soaked into the underlying rock

Surface Water is water collecting on the ground or in a stream, river, lake, or wetland.

Surface water is naturally replenished by precipitation and naturally lost through

discharge to the oceans, evaporation, and sub-surface seepage into the groundwater.

Surface water is the largest source of fresh water.

Tap water in this text means any natural or artificially produced water or a mixture of both,

which is certified fit to drink by the water works department and supplied to location by

means of a Government's main system.

Polished water in this text means water which has been purified and filtered by means of a

reverse osmosis polishing plant.

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)

APPENDIX 2 REQUEST FOR RESEARCH IN STATE SCHOOLS

Dim;;oni ta'1-Bdubzzjoni Dipartiment la' I-Ippjmar u tvilupp n-FurjIlJla MALTA

Edw:ation 1)ivjsi0ll Dc:putmc:at of Planning FlorillJla

Request for Research in State Schools

Ar. (PIMu _lUOCK I.EITUS)

Surname: .l~N:tO ..... ?'-.f}.~@. ... Name: ........... f..mg;l,,, .......... .

I.D.CardNumbef: .•. Q9..l3B.c~.) ........ : Telephone: .... ~!1:9..1.~ ...... .

Address·····~8~·· .. ····T.r.~~····c.:~~r.y,..o.··············· .. · .... · .. · ....................... . ..................... ~~~~................................. PostCode.~.tQ

Faculty. M~~ .. ~.~~{1 Course: }A.~.%li~ ... ~fh. Year: .... 4-: .. (~) AreJJ/s of research: ... ~~::~§Tf?:'f ................................ .............................................. .

Aims ~fresean:h: (Underline as appropriIIte) Long Essay Dissertation ~ Publication . Oc..+-~

Estimated duration of research: .S~~~~. ..... Language used: .•. ~ .. l.~ \LsI.-)

Description of method to be used: ... ~.!?~.~ ... ~~~ ..... ~~.!,V.Q~~ .... ~ .. ~.l.ili~~'\ ... ~ ... ~$,.Q •• f.?d.:.f.?r~~ ...... ~~.~:.~'!~!=!O ........................ .

SchooVs where reseMch is to be carried out: .... ~~ ... ~ ... t1?~ ... .p.:!~ ........ ~ ... ~~~~............... . .................................................... .

Years I Forms: .~.L~.~1-.~.t-"":1 Age range of students: .~:{q.~ .. ~: .. 9:· ...

I accept to abide by the rullllIId reguIdOns IV RaadI in SI* Sc:hooIIIIId to CCJn1IIY willi the Data PnJtedIon Ad. 2001.

Wl!nlnq to l!II!!icIntI-Arrt faR staIIment,. rniINprIIInIIII of COIICtIIImInt 01 matinJ fIc:t 011 this form or fir! document preI8IIt.d In IIIpport of this appIclllicla INIY be grounds for crlninal prosecution.

si_or_ ...... 'l/Iiilt .............................. D ... ,05Pb ·,Db

DPIDI2OO3· Rcsean:h &: PllDlling

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B. Tutors Approval (where applicable)

The above research work is being carried out under my supervision.

, ~\JU\ ~~AU.O . Tutor s Name: ........................ SIgnature ....... .. ( hi bIod; l«ten )

C. Education Division - Official Approval

00nIUItant c)eota\ Public Health

Official Stamp

The above request for permission to cany out research in State Schools is hereby approved according to the official rules and re~tioDS. c! _ \ _ " 0 l\.a 1\ ,.., n • ~ -. • ~~~~ ~~ ~~,~~0fH'~14

I\:} .J..!lI'to-. ~ Ra~'mond Camilleri

ASSIStIIIt Ditet:tor Reaan:h & Pfanning

Date: 0 I / tJ6 /C6 Official Stamp

Coaditions for tile approvalofa request by a student to grry oat mears. lI'Ork jp Sta1e Se ••

Permission for research in State Schools is Sllbject to the following conditions:

I. The official request form is to be accompanied by a copy of the questioonaire and I or any relevant material intended for use in schools during research work.

2. The original request form, showing the relevant signatures and approval, mUst be presented to the Head of School

3. All research work is carried out at the disaetion of the relative Head of School and subject to their conditions.

4. Researchers are to observe strict confidentiality at all times.

5. The Education Division reserves the right to withdraw permission to carry .out research in State Schools at any time and without prior notice.

6. Students are expected to res1rict their research to a minimwn ohtudents I teachers I administrators I schools, and to avoid any waste of time during their visits to schools.

7. As soon as the research in question is completed, the Education Division assumes the right to a full copy (in print Ion C.D.) of the research WoB: carried out in State Schools. Researchen are to fOl'fI'Ilnl tile copies to the Assistant Direetor Researeh and Plagging, EdIlQtio. Divisio ••

8. Researchers are to hand a copy of their Research in print or on C.D. to the relative Scboolls.

9. In the case of video recordings, researchers have to obtain prior permission from the Head of School and the teacher of the class concerned. Any adults recognisable in the video are to give their explicit consent.. Parents of students recognisable in the video are also to be requested to approve that their siblings may be video-recorded. Two copies of the consent fonus are necessary, one copy is to be deposited with the Head of school, and the other copy is to accompany the Request Form for Research in State Schools. Once the video recording is completed, one copy of the videotape is to be forwarded to the Head of school. The Education Division reserves the right to request another copy.

DPlDf2003- Research &: Planning 2

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APPENDIX 3 LETTER FROM UNIVERSITY RESEARCH ETIllCS COMMITTEE

L-UNlVERSITA: T8 MALTA Msida - Malta SKOLA MBDIKA

IIBI'.T~

I L..: Ref=-N=o:~3212006=:=.::-__ --,I ..

IS· Septemba" 2006

Dr Ethel vento Zahra Amaryllis Triq Cicerun Marsaxlokk ZTN 10

Dear Dr Vento Zahra

UNIVERSITY OF MALTA Msida-Malta

MEDICAL SCHOOL

Please refilr" to your' ~ submitted to the Research Ethics Committee in CODDeCtion with your research entided:

AN ASSESSMENT OF DENTAL FLUOROSIS IN GOZO

The University Research Ethics Committee at its meeting of 14'" July approved the abov&-mentioned Protoool. .

Yours sincerCly

Dr M Vassallo Cbairmao Research Ethics Committee

TEL: (356) 21333903-6. 21336451 CABLES: UNIVl!JISI1Y-MALU TELEX: <1117 HIEDUCMw FAX: (356) 21336450 MEDICAL SCHOOl., GWAIlDAMANGIA TEL: 21221019. 212m1l3 PAX: (0103'56) 21235638

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Angmar-Mansson, B.; Whitford, G.M.: Environmental and physiological factors affecting dental fluorosis. J. Dent. Res. 1990, v.69, p. 706-713.

Avery lK.. Agents affecting tooth and bone development. In: Avery lK., ed. Oral development and histology. 2nd Ed. New York, NY: Theime Medical Publishers, 1994: 130-141.

Baelum, V., Fejerskov, 0., Manji, F. & Larsen M.J.: Daily Dose of Fluoride and Dental Fluorosis, Danish Dental Journal 1987; 91, 452-456.

Bagramian, RA.: A 5-year school-based comprehensive preventive programme in Michigan, u.S.A. Community Dental Oral Epidemiology 1982; 10,234-37.

Bawden, J.W.: Changing patterns in systemic fluoride intake, Journal of Dental Research 1992;71,1212-1265.

Birch, S.: The relative cost-effectiveness of water fluoridation across communities. Analysis of variation according to underlying caries levels. Community of Dental Health 1990; 7, 3-10.

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Bowden, G.H. W.: Effects of fluoride on the microbial ecology of dental plaque. Journal of Dental Research 1990; 69 (Special Issue), 653-59.

Bratthal, D.; Hansel-Peterson, G; and Sundberg, H.: "Reasons for the Caries Decline: What Do the Experts Believe?" European Journal o/Oral Science 1996; 104:416-422.

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Burt, B.A., Eklund, SA., & Loesche, W.J.: Dental benefits of limited exposure to fluoridated water in childhood. Journal of Dental Research 1986; 61(11), 1322-1325.

Burt, B.A. & Eklund, S.A.: Dentistry, Dental Practice and the Community 1992; 4th edition.

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Butler W, Segreto VA, and Collins EM: Prevalence of dental mottling in school- aged lifetime residents of 16 Texas communities. American Journal of Public Health 1985, 75:1408-1412

Buzalaf, M.A.R, Cury J.A & Whitford G.M: Fluoride Exposures and Dental Fluorosis: A literature Review, 2001. Centres for Disease Control and Prevention: Recommendations for using fluoride to prevent and control dental carles in the United States. MMWR Morbid Mortal Wldy Rep 2001; 50:1-42.

Churchil~ KV.: Letter to McKay, F.S. In the McKay papers; 1931. Cited by McNeil; 1957, p.26.

Clark DC, Hann HJ, Williamson MF, Berkowitz J. Aesthetic concerns of children and parents in relation to different classifications of the Tooth Surface Index of Fluorosis. Community Dent Oral Epidemiology 1993; 21:360--4.

Clark D.C: Trends in prevalence of dental fluorosis in North America. Comm. Ent. Oral epidemiology 1994; vol 22 p.148-155.

Clarkson, B.H.: Caries prevention - Fluoride, Advances in Dental Research 1991; 5, 41-45.

Clarkson, J.: A European view of fluoride supplementation. British Dental Joumall992; pg 357.

Colquhoun J.: Why I changed my mind about Fluoridation. Perspectives in Biology and Medicine 1997; 41:29-44.

Council of European Chief Dental Officers (CECDO): Database of Oral Healthcare in Europe, 2004.

Crichton Browne, J.: Address to the Annual General Meeting of the Eastern Counties Branch of the British Dental Association. Journal of British Dental Association 1892; 13, 404-416.

Curzon MEJ, Spector PC: Enamel mottling in a high strontium area of the USA. Community Dental Oral Epidemiology 1977, 5: 243-247 Dean, H.T.: Chronic endemic dental fluorosis (mottled enamel). Journal of the American Medical Association 1936; 107, 1269-72.

Dean HT, McKay FS: Production of mottled enamel halted by a change in common water supply. Am J Public Health 1939; 29:590-596

Dean, H.T., Arnold, F.A. Jr & Elvove, E.: Domestic water and dental caries, v. additional studies of the relation of fluoride domestic waters to dental caries experience in 4425 white children aged 12-14 years, of21 cities in 4 states. Public Health Report 1942; 57, 1155-79.

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DenBesten PK, Thariani H. Biological mechanisms of fluorosis and level and timing of systemic exposure to fluoride with respect to fluorosis. J Dent Res 1992; 71: 1238-43.

Denbesten, P.K: Dental fluorosis: Its use as a biomarker, Adv. Dent. Res. 1994, V.8, n.l, pl05-110

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