womens_health.gif (1647 bytes)
Child Care Report
Golden Years
Environmental Health - Water
  1. Introduction
  2. Sources of Water in SEHB
  3. Contamination of Water Supply
  4. Microbiological Contamination
  5. Chemical Contamination
  6. Pesticides
  7. Conclusion
1. Introduction

The presence of safe and reliable source of water is an essential prerequisite for a healthy environment. Clean water is a resource that has often been taken for granted. Pure water is necessary for growing food, manufacturing goods, disposing of wastes, and for consumption. The objective of water treatment is to produce an adequate and continuous supply of pure and palatable water that must be -

Clean - no fine mineral or organic matter in suspension,

Colourless and odourless,

Palatable - no unpleasant taste,

Safe - no harmful organisms nor undesirable dissolved content,

Reasonably soft - no excessive amounts of soap-consuming mineral salts.

National and EU bodies with the purpose of protecting the health of the population, have prepared air water and food quality standards and guidelines. The main objective of this chapter is to compile a picture of the present state of drinking water (water intended for human consumption) in the South Eastern Health Board.

It is the duty of each of the seven Sanitary Authorities, which include County Councils and Urban District Councils, in the SEHB to take the necessary measures to ensure that, water intended for human consumption meets the quality standards of the EU Regulations. This refers both to drinking water and to supplies intended for use by food premises. Although the Sanitary Authority has the primary responsibility for the management of water resources, the Health Board, as part of its preventive health and infection control duties has a direct interest in the continuing purity of drinking water. The SEHB through its public health role has a major part in identifying threats to health, in responding to them and it becomes involved in dealing with health problems once they have occurred.

Over the years the pollution load of most receiving waters has increased. In addition to pollution from point sources, pollution from non-point (diffuse) sources, for example leaching and run off from agricultural areas, has become increasingly important.

Gross pollution (point source) of the nation's water ways is occurring less frequently. It is clear that to continue the progress made over the past decade, efforts must now focus on non-point source (NPS) pollution. The task of controlling NPS pollution is in many respects more difficult than controlling pollution from point sources. Non-point source pollution is quite diffuse, both in terms of its origin and in the manner in which it enters ground and surface water. It results from a variety of human activities that take place over a wide geographic area, perhaps many hundreds or thousands of acres. Unlike pollutants from point sources - which enter the environment at well defined locations - pollutants from non point sources usually find their way into surface and ground water in sudden surges, often in large quantities, and are associated with rainfall, thunderstorms and snowmelt.

2. Sources of Water in SEHB

There are three categories of source water for drinking water: groundwater, surface springs and surface water. In Ireland approximately 75% of the main public supplies are abstracted from surface water and 25% from ground sources. In the SEHB, four fifths (78%) of the public water supplies, are abstracted from surface sources and a fifth (22%) from ground water and surface springs (Figure 7.1). Waterford and Wexford County Councils source the highest percentage of their public water supply from ground water sources which accounts for nearly a third of their supply. The other Sanitary Authorities abstract approximately 10% of their supply from groundwater sources.

Table 7.1 Source of Drinking Water for Public water supplies in the SEHB

Area Surface water S/Spring water Ground water
Population % Population % Population %
Carlow Co.Council

30,300

90%

0

0%

3,400

10%
Kilkenny Co.Council

36,750

80%

4,050

9%

5,300

11%
Clonmel Corporation

15,125

100%

0

0%

0

0%
Tipperary SR.

43,691

75%

8,035

14%

6,662

11%
Waterford Co. Borough

42,450

100%

0

0%

0

0%
Waterford Co.Council

22,381

54%

6,616

16%

12,090

30%
Wexford Co.Council

55,442

71%

0

0%

22,756

29%
SEHB

258,969

79%

18,701

6%

50,208

15%

Source: EPA report: The quality of drinking water in Ireland, 19962

Public and private supplies
Approximately four fifths of the SEHB population are served by water from public supplies (Figure 7.2). A percentage of group supplies receive water from the local Sanitary Authority but are not under the control of the Sanitary Authority. This is the case in Carlow, Kilkenny, Wexford and Tipperary SR while in Waterford County Councils the majority of supplies are under control of the Sanitary Authority.

Table 7.2 Percentage of population of each Sanitary Authority supplies by public water supply

Sanitary Authority Total Population
1996 Census
Population served by Public water Supply Percentage
Carlow Co.

41,616

33,700

81%

Kilkenny Co.

75,336

46,100

61%

Tipp. SR and
Clonmel Corp.

75,514

66,751

89%

Waterford Co. and
Waterford Co. Bor.

94,680

91,087

96%

Wexford Co.

104,371

78,198

75%

SEHB

391,517

315,836

80%

Source: EPA report: The quality of drinking water in Ireland, 1996 & Tipperary SR County Council.

Monitoring and the extent of sampling is a function of the size of a population served by a given supply - the greater the number of consumers the more frequent and extensive must be the analysis. For supplies serving 1,000 persons and upwards there are a stated number of samples required to be taken in the year. However for supplies to consumers numbering less than 1,000 the degree of sampling and analysis is at the discretion of the Sanitary Authorities. The population of each Sanitary Authority on water supplies greater than 5,000, water supplies serving 1,000 - 5,000, and water supplies serving less than 1,000 persons is shown in Table 7.3.

In the SEHB 25% of the population is supplied with drinking water from supplies which serve less than 1,000 persons, of which less than one fifth are under the control of the local Sanitary Authority. This water commonly only receives rudimentary treatment and many small private water supplies have been shown to fall below microbiological standards so presenting a risk of faecal-oral disease transmission. However, these supplies are unlikely to produce a large scale risk, given the small number of consumers supplied from each source.

Drinking water supplied by group water schemes, or supplies to individuals families or to small groups of consumers are less likely to have disinfection (chlorination) equipment or if available may not be maintained or in use. These supplies are at risk of being contaminated from such sources as improperly sited septic tanks and/or animal slurry pits. This situation should improve as grants are now been provided to improve group schemes.

Table 7.3 Population of each Sanitary Authority served by size of water supply

Sanitary Authority

Public Water Supply

Private

Total Population

Population
> 5,000
Population 1,000-5,000 Population <1,000 Population <1,000
Carlow Co. 20,000 11,600 2,100 7,916 41,616
cleardot.gif (846 bytes) (48%) (28%) (5%) (19%) cleardot.gif (846 bytes)
Clonmel Corp. 15,215 - - - 15,215
cleardot.gif (846 bytes) (100%) - - - cleardot.gif (846 bytes)
Kilkenny Co. 24,000 21,900 200 29,236 75,336
cleardot.gif (846 bytes) (32%) (29%) (0.27%) (39%) cleardot.gif (846 bytes)
Tipp. SR 35,059 20,358 2,971 1,911 60,299
cleardot.gif (846 bytes) (58%) (34%) (5%) (3%) cleardot.gif (846 bytes)
Waterford Co. Bor. 42,540 cleardot.gif (846 bytes) cleardot.gif (846 bytes) cleardot.gif (846 bytes) 42,540
cleardot.gif (846 bytes) (100%) cleardot.gif (846 bytes) cleardot.gif (846 bytes) cleardot.gif (846 bytes) cleardot.gif (846 bytes)
Waterford Co. 20,000 12,096 8,991 11,053 52,140
cleardot.gif (846 bytes) (38%) (23%) (17%) (21%) cleardot.gif (846 bytes)
Wexford Co. 68,000 5,800 4,398 26,173 104,371
cleardot.gif (846 bytes) (65%) (6%) (4%) (25%) cleardot.gif (846 bytes)
SEHB Total 224,814 71,754 18,600 76,286 391,517

* percentages rounded to nearest whole number, therefore total may not be 100%

 

3. Contamination of water supply

The essential role of water in supporting human life means that, if contaminated, it has the potential for transmitting a wide variety of disease and illnesses.

It depends both on the original quality and also how water is protected at source, in transit, in storage, and in distribution as to whether or not water will reach the consumer in pure condition. Heightened public concerns over environmental pollution has increasingly focused on drinking water quality. The main source of potential contamination are industrial, agricultural and sewage.

The main pollution threats to water are -

A wide range of inorganic and organic contaminants from point source in urban, industrial, mining and landfill areas,
Leaching of nitrates,
Leaching of pesticides,
Acidification,
Microbiological Contamination.

4. Microbiological Contamination

Contamination of drinking water with microbiological agents can be a source of a variety of communicable diseases. With few exceptions, the major water borne diseases are transmitted by contamination of water supplies with infected human faeces or urine, so for practicable purposes a safe water supply is one protected from contact with human or other excreta and treated to destroy any pathogenic organisms inadvertently introduced. Infectious disease caused by contaminated drinking water is rare in the South Eastern Health Board.

 

4.1  Total & Faecal Coliforms
It is self-evident that water intended for drinking water must not contain agents of waterborne disease. However many pathogens, including bacteria, viruses and parasites, are difficult or even impossible to detect. Microbial indicators of water quality i.e. bacteria indicating either the potential for faecal pollution or that such pollution has occurred, are used, since their presence shows that pathogens could also be present. The most numerous of the faecal indicator bacteria is the coliform group, and the most suitable member of this group is the Escherichia coli (E.Coli), since it alone is derived exclusively from the faeces of humans and warm blooded animals. In practice E. coli should not be detectable in any 100 ml sample of any water intended for drinking.

Table 7.4 shows the number of exceedances for total and faecal coliforms in each Sanitary authority in 1996. Many of supplies showing coliform exceedances are from sources where chlorination has been installed. Stricter control of all existing chlorination facilities would bring about a substantial improvement in drinking water. It is important for Sanitary Authorities to maintain sufficient levels of residual chlorine at the consumers tap and also avoid elevated chlorine levels with resulting taste and odour problems.

Examples of micro-organisms known to have caused water borne infection include -

  • Campylobacter species,
  • Escherichia coli (certain serotypes),
  • Salmonella species (including S. typhi),
  • Shigella species,
  • Streptobacillus moniliformis,
  • Vibrio species,
  • Crytosporidium species,
  • Hepatitis A.

 

Table 7.4  Analysis of results of monitoring of Total / Faecal Coliforms Units No / 100mls

Sanitary Authority Number supplies Number of samples Total coliform <10 Total coliform >10 Total &
faecal coliforms
Carlow Co. 9 161 7 0 2
Kilkenny Co. 15 553 40 0 29
Clonmel Corp. 2 53 1 1 1
Tipp. SR 24 320 18 1 22
Waterford Corp. 1 109 0 1 1
Waterford Co. 105 267 17 3 13
Wexford Co. 57 458 33 5 33
SEHB Total 213 1,921 116 11 101

Source: EPA report: The quality of drinking water in Ireland, 1996

The South Eastern Health Board and Kilkenny County Council have developed a protocol for responding to microbiological incidents affecting water intended for human consumption. The protocol outlines clearly the steps to be taken when an infringement occurs. A timely response to infringements is essential and further investigation is instigated when residual chlorine levels are low or on when 'presumptive' coliforms are detected in any sample. If these investigations show evidence of actual or potential microbiological contamination, then effective remedial action is instituted immediately to ensure that satisfactory microbiological conditions are restored.

Efforts are continuing to gain acceptance by other local authorities of this protocol so that a 'Best Practice' approach can be implemented.

4.2  Cryptosporidium
Cryptosporidium is a microscopic, single celled parasite, which if swallowed can cause diarrhoea in animals and humans. Over the past ten years the public health significance of crytosporidium in water supplies has become much clearer, with several major outbreaks of waterborne crytosporidiosis being characterised, particularly in the UK and the USA. The cysts are normally removed by sand filtration, but this cannot be guaranteed and they are highly resistant to chlorine so that normal disinfection methods are unlikely to kill the organisms.

It is important, in the case of river or surface water abstraction, that specific allowance is made for this risk in any water treatment process. About 10% of isolates of diarrhoea (Figure 6.2) in the SEHB are caused by Crytosporidium, although the majority of these are due to direct infection from animals, including human transmission.

 

5. Chemical Contamination

The potential health hazards of chemical water pollution are also significant. Because of the solvent properties of water many substances may be found in solution in natural waters and some of them are potentially hazardous to human health. Fortunately the concentrations of most potentially harmful impurities in natural water are normally very low but there are thousands of compounds used in agriculture, in the home and in industry which can find their way into surface and ground waters.

There are two types of chemical effects - (1) acute effects where the consequences of consumption of the contaminated water are immediately apparent, and (2) chronic effects where continued ingestion of the contaminated water products produces a long-term hazard.

5.1 Nitrates
Nitrate nitrogen occurs naturally in many soils and is thus found in most groundwaters and in many surface waters. Increased use of artificial nitrogen fertiliser has raised the level of nitrate run off from farm land. As a result the levels of nitrates in water supplies have increased, particularly in areas subject to intensive arable farming. Sewage effluents also contain sufficient amounts of nitrogen which is often in the nitrate form.

Nitrates in drinking water can be dangerous for bottle fed babies up to the age of about six months. Below this age babies do not have the normal bacterial flora in their intestine, and they are unable to deal with the nitrites produced by the reduction of nitrate in the stomach. Elevated levels of nitrates can cause methaemoglinaemia or 'blue baby syndrome', a rare blood condition.

There is thought to be an elevated risk of cancer due to high levels of nitrate, but epidemiological studies have failed to support this contention. Recent epidemiological data has suggested an association between developmental effects in offspring and maternal ingestion of nitrate from drinking water, but a definite correlation of the cause and effect relationship cannot be drawn.3

To prevent unnecessary exposure, regulatory standards and advisory levels have been established in the EU drinking water guidelines. Monitoring data of nitrates in groundwater is supplied by each sanitary authority. Alternate sources of supply may be necessary when drinking water sources contain nitrate at levels higher than the maximum allowable concentration (MAC).

In the SEHB in 1996, analysis of the results of monitoring of nitrates in 166 of the public water supplies in the seven sanitary authorities in the SEHB, showed that less than 1% (4 out of 486 tests) showed exceedances, (Table 7.6).

5.2  Fluoride
Fluoride occurs naturally in some waters and its presence in drinking water has been shown to be inhibitory to tooth decay, particularly when young children are exposed. Under the Health (Fluoridation of water supplies) Act 1960, fluoride is added to public water supplies to reduce dental cavities. The practical and scientific evidence leaves no room for doubt on the benefits to dental health arising from fluoridation to a concentration of 1 mg/l.

While the EPA report highlights the number of exceedances based on Irish MAC value of 1 mg/l, this level is stricter than the EU Directive, which gives a MAC of 1.5 mg/l. At levels of fluoride above 1.5 mg/l there is a possibility of yellow staining of teeth and at much higher levels there is a danger of bone damage through fluorosis.

From the dental benefit of fluoridation, the health Board is concerned that Sanitary Authorities maintain adequate levels in the PWS (0.8 - 1 mg/l). There are far more incidences of inadequate fluouridation of water supplies than of exceedances. The number of exceedances of fluoride by Sanitary Authority is shown in table 7.6.

Fluoride mouth washing is helpful in providing fluoride to the children who live in areas with non fluoridated water.

Table 7.5 Fluoride Mouth Rinse programme SEHB

Community Care Area Number of Schools on programme Total in rinse Programme
(>7 years)
Population Children
7-12 years*
Carlow/Kilkenny 39 1,888 12,356
Tipperary SR 19 1,571 7,872
Waterford 28 1,338 9,319
Wexford 58 3,880 11,000
SEHB Total 144 8,677 40,547

*1996 Census

In the SEHB a mouth wash scheme operates in areas where supplies are not fluoridated. The numbers of children in this shown is shown in table 7.5.

5.3  Lead
Lead levels in untreated natural waters are normally very low and the lead in drinking water is almost entirely due to lead pipes in household plumbing, especially in combination with soft water. Excess levels of lead may slow mental development in children.

In 1996, 0f 150 samples determined for lead only one was in excess of the MAC.

It is proposed in the revised drinking water directive by the EU commission to reduce from 50 mg/l to 10 mg/l the maximum permitted concentration of lead in drinking water.

5.4  Aluminium
Aluminium occurs naturally in some raw water sources and it is commonly used as a coagulant in water treatment processes. In normal circumstances the aluminium is converted to an insoluble form and is thus removed from the water. It is important that residual levels remain well below the maximum admissible concentration of 0.2 mg/l.

It has been suggested that there might be an association between aluminium in water supplies and dementia; however there is no firm evidence to support this. A specialised health hazard arising from the presence of aluminium in the water is that patients on kidney dialysis machines can be fatally affected if the supply to the machine contains soluble aluminium.

In 1996, in the SEHB, 104 samples were checked for aluminium in 34 supplies. Of these 21 (20%) exceeded the MAC (Figure 7.6). Most of these exceedances were in the concentration band just above the MAC and thus not greatly over the limit.

Seven of the exceedances were in the Borris supply in Carlow, which is largely due to high background levels of aluminium in the raw water. Ten of the exceedances were in the three PWSs that use coagulation in the treatment process in South Tipperary.

Under the Environmental Protection Agency (EPA) Act 1992, the EPA is responsible for preparing a report each year, on drinking water quality in Ireland for the Minister for Environment. The data in the report are based on data provided by the Sanitary Authorities. The latest report from the EPA is for the year 1996. Exceedances by parameter in each Sanitary Authority are shown in table 7.6.

Table 7.6  Analysis of exceedances by Parameter in Public Water Supplies in Local authorities in SEHB - 1996

Carlow Co. Council Clonmel Corp Kilkenny Co. Council Tipp. SR Co. Council Waterford Corp.   Waterford Co. Council Wexford Co. Council  
Number of Supplies 9 2 15 24 1 106 57
Number of Samples 173 54 569 320 109 267 512
Aluminium 7 - 1 10 - 2 1
Ammonium - - - - - - 1
Coliforms 9 3 69 41 2 31 71
Colour   4 6 12 42 - 3 2
Fluoride 3 10 23 16 - 4 16
Iron - 2 6 17 - 7 2
Manganese  - - 3 13 - 1 3
Nitrates 1 - 2 - - 1 -
Nitrites - - - - - - -
Odour   18 - 3 - 3 1 -
PH 2 - 2 17 - 28 2
Taste - - - - - - -
Turbidity - - - 14 - 3 1

Source: EPA report: The Quality of Drinking Water in Ireland - 1996

6.  Pesticides

Approximately 600 pesticides (as broadly defined to include herbicides as well as fungicides and insecticides) are applied in agriculture, silviculture and horticulture. On their passage through the sub-surface environment, these 600 active ingredients are transformed into an (unknown) number of degradable products (residues). The effects of active ingredients and their residues on non-target terrestial organisms (side effects), their fate in the soil and their undesired effects in groundwater are far from known with certainty for every substance. Only a few pesticide measurements in groundwater are available for a restricted number of constituents. Out of approximately 600 pesticides, only about 30 have been monitored. These 30 pesticides are neither the most mobile, nor representative of all pesticides.

The results of a preliminary survey of Pesticides in Drinking Waters in 1994-1995, by the Environmental Protection Agency4 was reported in 1996. Taking the results as a whole, there was no significant background level of any of these compounds in Irish drinking waters. Five positive residues (over 0.1 ug/1) were obtained from a total of over 3,300 analytical results. However these five results indicate that there is a real possibility of intermittent short-term contamination which needs to be considered.

 

7.  Conclusion

The maintenance of wholesome drinking water supplies requires the commitment of individuals from many different disciplines: professionals in Sanitary Authorities, public health specialists, environmental health officers, public analysts and hospital microbiologists. Good communication and liaison between all these individuals is essential to enable appropriate action to be taken whenever water quality problems occur.

It is recommended that:

That a protocol for responding to infringements in water quality be agreed with all Sanitary Authorities in the SEHB region.

References

1 Environmental Protection Agency. The Quality of Drinking Water in Ireland, a report for the
   year 1996. Environmental Protection Agency, Wexford, 1996.
2 European Communities (quality of water intended for human consumption)Regulations, 1988.
3 Fan AM, Steinberg VE. Health Implications of Nitrate and Nitrite in Drinking Water: An update
  on Methemoglobinaemia Occurrence and Reproductive and Development Toxicity. Regulatory
  Toxicology and Pharmacology 1996; 23:35-43.
4 Environmental Protection Agency. Pesticides in Drinking Water. Result of preliminary survey
  December 1994 -December 1995. Environmental Protection Agency, Ardcavan, Wexford,
  1996.
5 HMSO, Drinking Water Supplies: A Microbiological Perspective. Dawson A, West P, (eds)
  London HMSO 1993.
6 HMSO. The Microbiology of Water 1994 Part 1 - Drinking Water. Report on Public Health and
  Medical Subjects No. 71. HMSO, London 1994.

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