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| Environmental Health - Water |
- Introduction
- Sources of Water in SEHB
- Contamination of Water Supply
- Microbiological Contamination
- Chemical Contamination
- Pesticides
- Conclusion
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| 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. |
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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 |
 |
(48%) |
(28%) |
(5%) |
(19%) |
 |
| Clonmel Corp. |
15,215 |
- |
- |
- |
15,215 |
 |
(100%) |
- |
- |
- |
 |
| Kilkenny Co. |
24,000 |
21,900 |
200 |
29,236 |
75,336 |
 |
(32%) |
(29%) |
(0.27%) |
(39%) |
 |
| Tipp. SR |
35,059 |
20,358 |
2,971 |
1,911 |
60,299 |
 |
(58%) |
(34%) |
(5%) |
(3%) |
 |
| Waterford Co.
Bor. |
42,540 |
 |
 |
 |
42,540 |
 |
(100%) |
 |
 |
 |
 |
| Waterford Co. |
20,000 |
12,096 |
8,991 |
11,053 |
52,140 |
 |
(38%) |
(23%) |
(17%) |
(21%) |
 |
| Wexford Co. |
68,000 |
5,800 |
4,398 |
26,173 |
104,371 |
 |
(65%) |
(6%) |
(4%) |
(25%) |
 |
| 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. |
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| 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. |

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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. |

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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 |

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| 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 Agency 4 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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