Drinking Water Parameter Information Explained
The table below lists each of the drinking water parameters specified by the EC (Drinking Water) (No.2) Regulations, 2007. These are divided into three groups, i.e. Microbiological, Chemical and Indicator parameters. Within each of these groups the parametric value is listed (i.e. the regulatory value which must not be exceeded), the units of measurements and comments explaining the significance of each parameter. Also included are details of the monitoring category, check monitoring is carried out more frequently than audit monitoring.
|
|
Parametric
value |
Unit |
Comments |
Notes |
Monitoring
Category |
|||
|
Check |
Audit |
|||||||
|
1 |
Escherichia coli (E. coli) |
0 |
No./100ml |
The E. coli bacteria is present in very high numbers in human or animal faeces
and is rarely found in the absence of faecal pollution.
As such, its presence in drinking water is a good indication that either
the source of the water has become contaminated or that the treatment process at
the water treatment plant is not operating adequately.
|
|
Yes |
Yes |
|
|
2 |
Enterococci |
0 |
No./100ml |
Enterococci originate in human
or animal waste and thus their presence provides an indication that the water supply
has been contaminated with faeces |
|
|
Yes |
|
|
|
||||||||
|
3 |
Acrylamide |
0.10 |
mg/l |
Acrylamide can be present in water supplies from the use of polyacrylamides as coagulant
aids in water treatment. It is classified
by the International Agency for Research on Cancer (IARC) in Group 2A (i.e., probably
carcinogenic to humans).
|
Note 1 |
|
|
|
|
4 |
Antimony |
5.0 |
mg/l |
Antimony is a naturally occurring trace element used in the metal industry and in
flame retardant materials. It can also
occur naturally from weathering of rocks.
The toxicity of antimony depends on the form it occurs in (naturally occurring antimony
is likely to be in the less toxic form) and while there is some evidence for the
carcinogenicity of certain antimony compounds by inhalation, there is no data to
indicate carcinogenicity by the oral route. |
|
|
Yes |
|
|
5 |
Arsenic |
10 |
mg/l |
Arsenic is widely distributed through-out the Earth’s crust and is used in certain
industrial applications (primarily as alloying agents in the manufacture of transistors,
lasers and semi-conductors) and has been used in the past as a component of the
wood preservative CCA (Copper-Chromium-Arsenic) though it is no longer in use. However, the primary source of arsenic
in drinking water is from its dissolution into groundwater from naturally occurring
ores and minerals.
Arsenic has been shown to have significant health effects in some parts of the world
(e.g.
|
|
|
Yes |
|
|
6 |
Benzene |
1.0 |
mg/l |
The principle source of benzene is from vehicle emissions which may find their way
into water. Benzene is carcinogenic
to humans.
|
|
|
Yes |
|
|
7 |
Benzo(a)pyrene |
0.010 |
mg/l |
Benzo(a)pyrene was formerly included in the group of chemicals called PAHs (Polycyclic
Aromatic Hydrocarbons) which are generally undesirable in water.
The absolute undesirability of benzo(a)pyrene in drinking water has been
emphasised by its inclusion as a separate parameter.
It is carcinogenic.
|
|
|
Yes |
|
|
8 |
Boron |
1.0 |
mg/l |
Boron is a naturally occurring element and can occur naturally in groundwater. It is also used in the manufacture of
glass, soap, and detergents and as flame retardants.
Development toxicity has been demonstrated in laboratory animals at levels
in excess of the parametric value.
|
|
|
Yes |
|
|
9 |
Bromate |
10 |
mg/l |
Bromate is classified by the International Agency for Research on Cancer (IARC)
in Group 2B (i.e., possibly carcinogenic to humans).
Bromate is not normally found in water but may be formed during ozonation
when the bromide ion is present in water.
Under certain conditions, bromate may also be formed in concentrated hypochlorite
solutions used to disinfect water (WHO, 2004). |
Note 2 |
|
Yes |
|
|
10 |
Cadmium |
5.0 |
mg/l |
Cadmium is used in the steel and plastics industry and is a common component of
batteries. It may also enter water
from trace impurities in the zinc of galvanised pipes and solders and some metal
fittings. Cadmium can accumulate in
the kidneys.
|
|
|
Yes |
|
|
11 |
Chromium |
50 |
mg/l |
Chromium is commonly found in the Earth’s crust, though can be present in water
from contamination from timber treatment chemicals (Copper-Chromium-Arsenic). The toxicity of chromium depends on
the form in which it is found, with hexavalent chromium classified as a human carcinogen. |
|
|
Yes |
|
|
12 |
Copper |
2.0 |
mg/l |
Copper is a nutrient essential for health, though at elevated levels can become
a contaminant (elevated levels can cause acute gastrointestinal effects).
The primary source of copper in drinking water is from corrosion of internal
copper plumbing. The levels of copper
in drinking water depend on the length of time the water has been stagnant in the
copper piping and thus fully flushed water generally has low levels of copper.
|
Note 3 |
|
Yes |
|
|
13 |
Cyanide |
50 |
mg/l |
Cyanide is a reactive, highly toxic entity, which, in excessive amounts, will cause
mortality to humans. It is a common
constituent of industrial wastes, especially from metal plating processes and electronic
components manufacture.
|
|
|
Yes |
|
|
14 |
1,2-dichloroethane |
3.0 |
mg/l |
1,2-dichloroethane is a synthetic intermediate and organic solvent used in the manufacture
of chemicals. It can enter water from
discharges from facilities using the chemical.
It is a toxic substance which can cause a variety of ill-effects including
eye damage, dermatitis and narcotic effects.
It has also been classified by the IARC in Group 2 (possible human carcinogen).
|
|
|
Yes |
|
|
15 |
Epichlorohydrin |
0.10 |
mg/l |
Epichlorohydrin can be present in water supplies from the use of polyamines as coagulant
aids in water treatment and from epoxy resin linings of water mains and water retaining
structures. It is classified by the
International Agency for Research on Cancer (IARC) in Group 2A (i.e., probably carcinogenic
to humans).
|
Note 1 |
|
|
|
|
16 |
Fluoride |
0.8 |
mg/l |
Fluoride arises almost exclusively from fluoridation of public water supplies and
from industrial discharges, although it occurs naturally in quite rare instances.
Past health studies have shown that the addition of fluoride to water supplies at
levels above 0.6mg/l F- leads to a reduction in tooth decay in growing
children and that the optimum beneficial effects were thought to occur around 1.0
mg/l. However, in light of recent international and Irish research which shows an
increasing occurrence of dental fluorosis, the Forum on Fluoridation (2002) recommended
the lowering of the fluoride levels in drinking water to a range of 0.6 to 0.8 mg/l,
with a target of 0.7 mg/l.
|
Note 11 |
|
Yes |
|
|
17 |
Lead |
10 |
mg/l |
Lead is present in drinking water primarily from its dissolution from lead pipes
or lead-containing solder and thus the concentration of lead in drinking water depends
on a number of factors including pH, temperature, water hardness and standing time
of the water. Consequently, the method
of sampling for lead is critical and depending on the method used results can vary
significantly. According to the World
Health Organisation (WHO, 2004) lead is a general toxicant that accumulates in bone. Infants, children up to 6 years of age
and pregnant women are the most susceptible to its health effects.
It is toxic to both the central and peripheral nervous systems. |
Notes 3 and 4 |
|
Yes |
|
|
18 |
Mercury |
1.0 |
mg/l |
Mercury is a very toxic metal that primarily effects the kidney.
It has been used in electrical appliances, batteries, plastics and in dental
amalgams, though many of these uses are no longer applicable.
|
|
|
Yes |
|
|
19 |
Nickel |
20 |
mg/l |
Nickel is a metal used in the production of stainless steels and alloys and thus
may be present in drinking water from water that comes into contact with nickel
or chromium plated taps particularly where the water has been stagnant prior to
consumption. Nickel compounds are carcinogenic
and metallic nickel is possibly carcinogenic.
|
Note 3 |
|
Yes |
|
|
20 |
Nitrate |
50 |
mg/l |
Nitrate in the environment originates mostly from organic and inorganic sources
such as waste discharges, animal slurries and artificial fertiliser.
High levels of nitrate in drinking water may induce “blue baby” syndrome
(methaemaglobinemia). The nitrate converts
to nitrite which reacts with blood haemoglobin thus reducing the availability of
the blood to hold oxygen.
|
Note 5 |
|
Yes |
|
|
21 |
Nitrite |
0.50 |
mg/l |
Nitrites exist in very low levels principally because the nitrogen will tend to
exist in other forms (such as ammonia).
Nitrite is an intermediate in the oxidation of ammonia to nitrate.
Nitrite is associated with methaemaglobinemia as previously discussed.
|
Note 5 |
Yes* |
Yes* |
|
|
22 |
Pesticides |
0.10 |
mg/l |
Pesticides refers to a wide range of chemicals used for the control of pests. The parametric value is set on a precautionary
basis. Where pesticides are detected
the individual pesticide detected must be considered and its toxicology. |
Notes 6 and 7 |
|
Yes |
|
|
23 |
Pesticides – Total |
0.50 |
mg/l |
Pesticides refers to a wide range of chemicals used for the control of pests. The parametric value is set on a precautionary
basis. Where pesticides are detected
the individual pesticide detected must be considered and its toxicology. |
Note 6 and 8 |
|
Yes |
|
|
24 |
Polycyclic aromatic hydrocarbons |
0.10* |
mg/l |
Polycyclic Aromatic Hydrocarbons (PAHs) are a group of organic compounds containing
2 or more fused aromatic rings of carbon and hydrogen atoms.
Although there are many compounds in this group, for the purposes of determining
compliance with the Drinking Water Regulations only four are considered – benzo(b)fluoranthene,
benzo(k)fluoranthene, benzo(ghi)perylene and indeno(1,2,3-cd)pyrene.
They originate from many sources including coal-tar coating of drinking water
pipes, soot, vehicle emissions and as combustion products of hydrocarbon fuels. This group of compounds are widely regarded
as carcinogens, though the potency of the different PAHs varies. |
Note 9 |
|
Yes |
|
|
25 |
Selenium |
10 |
mg/l |
Selenium originates from the weathering of rocks and soils but is also used in industry
as a chemical catalyst. It is an essential
biological requirement though only very small concentrations of selenium are required,
above which it is toxic and can cause a variety of illnesses.
|
|
|
Yes |
|
|
26 |
Tetrachloroethene/Trichloroethene |
10* |
mg/l |
Tetrachloroethene and trichloroethene are synthetic solvents used in the dry-cleaning
industry and other various industrial and manufacturing processes as well as being
used as a degreaser. It may be carcinogenic
but otherwise can have a variety of ill effects.
|
|
|
Yes |
|
|
27 |
Trihalomethanes – Total |
100* |
mg/l |
Trihalomethanes (THMs) are derivatives of the simplest
organic compound - methane, CH4
- in which 3 of the hydrogen atoms are substituted by halogen atoms.
The principal halogens are fluorine (F2), chlorine (Cl2),
bromine (Br2) and iodine (I2), but while many combinations
are theoretically possible, the term trihalomethanes is applied to four specific
compounds containing only chlorine and/or bromine as the halogen elements.
The four compounds are chloroform
(CHCl3),
bromodichloromethane (CHBrCl2),
dibromochloromethane (CHBr2Cl) and
bromoform (CHBr3).
Chlorine (or appropriate compounds of it) is undoubtedly
the most important chemical used in water treatment in
As a powerful oxidising agent, chlorine also breaks
down the complex and inert organic molecules which are the colouring agents of the
water, forming smaller, reactive entities.
These entities react with chlorine (and with bromine derived from the oxidation
by chlorine of bromide naturally present) to form the THM compounds, the most abundant
of which is chloroform(CHCl3).
There is thus a fairly straightforward relationship between the degree of colour
in the water prior to chlorination and the quantities of THMs present following
chlorination. If colour is present
at the point of chlorination, THMs are likely to be formed.
THM compounds are undesirable in drinking water for
two reasons. Firstly, the actual compounds
themselves may pose a hazard to the health of the consumer if present in excessive
amounts, as chloroform is a suspected carcinogen.
Secondly, the presence of the THM group may be an indicator of the possible
presence of other organic by-products of chlorination in trace amounts. The WHO
advises that “In controlling trihalomethanes,
a multistep treatment system should be used to reduce organic trihalomethane precursors,
and primary consideration should be given to ensuring that disinfection is never
compromised”. |
Note 10 |
|
Yes |
|
|
28 |
Vinyl chloride |
0.50 |
mg/l |
Vinyl chloride can be present in water supplies from the use of unplasticised polyvinyl
chloride (uPVC) pipes in water distribution systems.
It is carcinogenic. |
Note 1 |
|
|
|
|
|
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|
29 |
Aluminium |
200 |
mg/l |
Aluminium is present in drinking water as a result of its use as aluminium sulphate
(a coagulant) in the water treatment process, though can be naturally present in
some waters. Historically, there has
been some concern about possible links between aluminium in drinking water and Alzheimer’s
disease. However, the WHO states that:
“On the whole, the positive relationship between aluminium
in drinking water and Alzheimer’s disease which was demonstrated in several epidemiological
studies, cannot be totally discounted.
However, strong reservations about inferring a causal relationship are warranted
in view of the failure of these studies to account for demonstrated confounding
factors and for the total aluminium intake from all sources”. |
|
Yes* |
Yes* |
|
|
30 |
Ammonium |
0.30 |
mg/l |
Ammonium in water supplies originates from agricultural and industrial processes,
as well as from disinfection with chloramines (a method of disinfection not in use
in
|
|
Yes |
Yes |
|
|
31 |
Chloride |
250 |
mg/l |
Chloride can originate from natural sources such as saltwater intrusion in coastal
sources but can be present in sewage and industrial effluents and thus can be an
indicator of pollution from these sources.
|
Note 12 |
|
Yes |
|
|
32 |
Clostridium perfringens
(incl spores) |
0 |
No/100 ml |
Clostridium perfringens
is a member of the bacterial intestinal flora of humans and therefore serves as
an indicator of faecal pollution. The
spores of Clostridium perfringens are particularly resistant to unfavourable
conditions in the environment and thus they survive for long periods.
As such they can be useful indicators of water that is intermittently polluted. |
Note 13 |
Yes* |
Yes* |
|
|
33 |
Colour |
Acceptable to consumers and no abnormal change |
|
Colour in water is usually due to the presence of complex organic molecules derived
from vegetable (humic) matter such as peat, leaves, branches etc.
While colour, in itself is primarily as aesthetic parameter it may indicate
other problems with the water supply particularly where the water is chlorinated. In such cases the formation of trihalomethanes
may occur. |
|
Yes |
Yes |
|
|
34 |
Conductivity |
2500 |
mS cm-1 at 20 0C |
Conductivity is a measure of the ability of water to conduct an electrical current,
therefore conductivity is related to the ionic content of the water.
|
Note 12 |
Yes |
Yes |
|
|
35 |
Hydrogen ion concentration |
³ 6.5 and
£9.5 |
pH units |
pH is a measure of whether a liquid is acid or alkaline.
The pH scale ranges from 0 (very acid) to 14 (very alkaline).
The range of natural pH in freshwaters extends from around 4.5 for acid peaty
upland waters to over 10 in waters where there is intense photosynthetic activity
by algae. However, the most frequently
encountered range is 6.5 to 8.0. The
control of pH is a critical component of water treatment and distribution, influencing
the effectiveness of coagulation, disinfection and the concentration of plumbing
materials (such as lead, copper and nickel) in the final product. |
Note 12 |
Yes |
Yes |
|
|
36 |
Iron |
200 |
mg/l |
Iron is an abundant metal found in the Earth’s crust.
It is naturally present in water but can also be present in drinking water
from the use of iron coagulants or the corrosion of steel and cast iron pipes during
water distribution. Iron is an essential
element in human nutrition. The WHO
(WHO, 2004) states that values of up to 2 mg/l (10 times the parametric value) do
not present a hazard to health. However,
at levels less than 2 mg/l but above the parametric value, the colour of water may
turn brown, become turbid or may deposit solids on clothes washed in the water or
food cooked using water.
|
|
Yes* |
Yes* |
|
|
37 |
Manganese |
50 |
mg/l |
Manganese is an element abundant in the Earth’s crust and is commonly found in groundwater. In common with iron, the problems associated
with levels of manganese above the parametric value are primarily aesthetic, as
manganese can cause staining problems.
High levels of manganese also cause objectionable tastes in the water but there
are no particular toxicological connotations.
The WHO recommend a guideline value of 0.4 mg/l, which is twice the parametric
value in the Regulations. |
|
|
Yes |
|
|
38 |
Odour |
Acceptable to consumers and no abnormal change |
|
|
|
Yes |
Yes |
|
|
39 |
Oxidisability |
5.0 |
mg/l 02 |
Oxidisability is a measure of the organic (and other oxidisable) matter present
in a water.
|
Note 14 |
|
|
|
|
40 |
Sulphate |
250 |
mg/l |
Sulphate is naturally occurring and is present in numerous minerals.
The WHO review (WHO, 2004) did not identify a level of sulphate in water
that is likely to cause adverse health effects but studies did indicate a laxative
effect at concentrations of 1,000 to 1,200 mg/l (i.e., several times higher than
the parametric value).
|
Note 12 |
|
Yes |
|
|
41 |
Sodium |
200 |
mg/l |
Sodium is an abundant natural constituent of rocks and soils and is always present
in natural waters. Excessive intake
can cause hypertension but the primary mode of intake is via food.
|
|
|
Yes |
|
|
42 |
Taste |
Acceptable to consumers and no abnormal change |
|
|
|
Yes |
Yes |
|
|
43 |
Colony count 220C |
No abnormal change |
|
This is the number of organisms per millilitre when the water is stored at 220C. The usefulness of this parameter is
that sudden or significant changes in the levels of organisms can indicate problems
with the water supply. |
|
|
Yes |
|
|
44 |
Coliform bacteria |
0 |
No./100 ml |
The coliform bacteria (previously know as Total Coliforms) are a group of organisms
that can survive and grow in water.
They are a useful indicator of treatment efficiency and the cleanliness of the distribution
mains. Coliform bacteria can occur
in sewage and in natural waters. Coliform
bacteria should not be present in a water that is disinfected and their presence
indicates that either disinfection has not been complete, that there is ingress
into the water mains in the distribution network or that the sample point is contaminated. |
|
Yes |
Yes |
|
|
45 |
Total Organic Carbon (TOC) |
No abnormal change |
|
This is a measure of the organic carbon in water.
Sudden or significant changes in the level of TOC in the treated water can
indicate problems with the water supply. |
Note 15 |
|
Yes |
|
|
46 |
Turbidity |
Acceptable to consumers and no abnormal change |
|
The control of turbidity is one of the indicators of the efficiency of treatment
at the plant. Elevated levels of turbidity
in the treated water indicate that the treatment process is not operating adequately. It also provides a good indication of
whether the treatment plant is capable of removing Cryptosporidium oocysts. While the parametric value for turbidity
(at the tap) is that the water must be “acceptable to consumers and [there
must be] no abnormal change” there is a parametric value for turbidity
(for water leaving the treatment plant) of 1.0 NTU.
However, it must be stressed that this value is for visual acceptability
of the water. In practice turbidity
levels need to be much lower and should not exceed 0.2 NTU and preferably be below
0.1 NTU to be protective against Cryptosporidium breakthrough in the treatment
plant. |
Note 16 |
Yes |
Yes |
|
|
47 |
Tritium |
100 |
Bq/l |
|
Notes 17 and 19 |
|
Yes |
|
|
48 |
Total indicative dose |
0.10 |
mSv/year |
|
Notes 18 and 19 |
|
Yes |
|
Notes
*
These parameters can be either check or audit
monitoring depending on the circumstances.
Note 1:
The parametric value refers to the residual monomer concentration in the
water as calculated according to specifications of the maximum release from the
corresponding polymer in contact with the water.
Note 2:
For the water referred to in sub-articles 6 (a), (b) and (c) the parametric
value to be met by 1 January, 2004 is 25
mg/l. A value of 10
mg/l
must be met by 25 December, 2008.
Note 3:
The value applies to a sample of water intended for human consumption obtained
by an adequate sampling method* at the tap and taken so as to be representative
of a weekly average value ingested by consumers and that takes account of the occurrence
of peak levels that may cause adverse effects on human health.
*The
Copper, Lead and Nickel parameters shall be monitored in such a manner as the Minister
shall determine from time to time.
Note 4:
For water referred to in sub-articles 6 (a), (b) and (c), the parametric
value to be met by 1, January 2004 is 25
mg/l. A
value of 10 mg/l must be met by 25 December, 2013.
All appropriate
measures shall be taken to reduce the concentration of lead in water intended for
human consumption as much as possible during the period needed to achieve compliance
with the parametric value.
When
implementing the measures priority shall be progressively given to achieve compliance
with that value where lead concentrations in water intended for human consumption
are highest.
Note 5:
Compliance must be ensured with the conditions that [nitrate]/50 + [nitrite]/3
< 1, the square brackets signifying the concentrations in mg/l for nitrate (NO3)
and nitrite (NO2) and the value of 0.10mg/l for nitrites ex water treatment works.
Note 6:
Only those pesticides which are likely to be present in a given supply require
to be monitored.
“Pesticides” means:
- organic
insecticides,
- organic
herbicides,
- organic
fungicides,
- organic
nematocides,
- organic
acaricides,
- organic
algicides,
- organic
rodenticides,
- organic
slimicides,
- related
products (inter alia, growth regulators)
and their
relevant metabolites, degradation and reaction products.
Note 7:
The parametric value applies to each individual pesticide. In the case of
aldrin, dieldrin, heptachlor and heptachlor epoxide the parametric value is 0.030
mg/l.
Note 8:
“Pesticides – Total” means the sum of all individual pesticides detected
and quantified in the course of the monitoring procedure.
Note 9:
The specified compounds are:
- benzo(b)fluoranthene
- benzo(k)fluoranthene
- benzo(ghi)perylene
- indeno(1,2,3-cd)pyrene.
Note 10:
The specified compounds are: chloroform, bromoform, dibromochloromethane
and bromodichloromethane.
For the
water referred to in sub-articles 6 (a), (b) and (c), the parametric value to be
met by 1 January, 2004 is 150 mg/l.
A value of 100 mg/l must be met by 25 December, 2008.
All appropriate
measures must be taken to reduce the concentration of THMs in water intended for
human consumption as much as possible during the period needed to achieve compliance
with the parametric value.
When
implementing the measures to achieve this value, priority must progressively be
given to those areas where THM concentrations in water intended for human consumption
are highest.
Note 11:
The parametric value is 1.0mg/l for fluoridated supplies.
In the case of supplies with naturally occurring fluoride the parametric
value is 1.5mg/l.
Note 12:
The water should not be aggressive
Note 13:
This parameter need not be measured unless the water originates from or is
influenced by surface water. In the
event of non-compliance with this parametric value, the supply shall be investigated
to ensure that there is no potential danger to human health arising from the presence
of pathogenic micro-organisms, e.g. cryptosporidium.
Note 14:
This parameter need not be measured if the parameter TOC is analysed.
Note 15:
This parameter need not be measured for supplies of less than 10,000m3
a day.
Note 16:
In the case of surface water treatment, a parametric value not exceeding
1.0 NTU (nephelometric turbidity units) in the water ex treatment works must be
strived for.
Note 17:
Monitoring frequencies to be set at a later date in Part 2 of the Schedule.
Note 18:
Excluding tritium, potassium –40, radon and radon decay products; monitoring
frequencies, monitoring methods and the most relevant locations for monitoring points
to be set at a later date in Part 2 of the Schedule.
Note 19:
A. The proposals required by
Note 6 on monitoring frequencies, and Note 7 on monitoring frequencies, monitoring
methods and the most relevant locations for monitoring points in Part 2 of the Schedule
shall be adopted in accordance with the Committee procedure laid down in Article
12 of Council Directive 98/83/EEC.
B.
Drinking water need not be monitored for tritium or radioactivity to establish total
indicative dose where, on the basis of other monitoring carried out, the levels
of tritium of the calculated total indicative dose are well below the parametric
value.