80-778 EEC欧盟饮用水水质标准(1980)
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?B COUNCIL DIRECTIVE
of15July1980
relating to the quality of water intended for human consumption
(80/778/EEC)
(OJ L229,30.8.1980,p.11)
Amended by:
Official Journal
Nopage date
?M1Council Directive81/858/EEC of19October1981L319197.11.1981?M2Council Directive91/692/EEC of23December1991L3774831.12.1991
Amended by:
?A1Act of Accession of Spain and Portugal L3022315.11.1985?A2Act of Accession of Austria,Sweden and Finland C2412129.8.1994 (adapted by Council Decision95/1/EC,Euratom,ECSC)L11 1.1.1995
Corrected by:
?C1Corrigendum,OJ L220,6.8.1981,p.40(80/778)
▼B
COUNCIL DIRECTIVE
of15July1980
relating to the quality of water intended for human consumption
(80/778/EEC)
THE COUNCIL OF THE EUROPEAN COMMUNITIES,
Having regard to the Treaty establishing the European Economic
Community,and in particular Articles100and235thereof,
Having regard to the proposal from the Commission,
Having regard to the opinion of the European Parliament(1),
Having regard to the opinion of the Economic and Social Committee(2),
Whereas,in view of the importance for public health of water for
human consumption,it is necessary to lay down quality standards with
which such water must comply;
Whereas a disparity between provisions already applicable or in the
process of being drawn up in the various Member States relating to the
quality of water for human consumption may create differences in the
conditions of competition and,as a result,directly affect the operation
of the common market;whereas laws in this sphere should therefore be
approximated as provided for in Article100of the Treaty;
Whereas this approximation of laws should be accompanied by
Community action designed to achieve,by more extensive rules
concerning water for human consumption,one of the aims of the
Community with regard to the improvement of living conditions,the
harmonious development of economic activities throughout the
Community and a continuous and balanced expansion;whereas certain
specific provisions to this effect should therefore be laid down;whereas
Article235of the Treaty should be invoked as the necessary powers
have not been provided for by the Treaty;
Whereas the1973(3)and1977(4)programmes of action of the Euro-
pean Communities on the environment provide for both the setting of
standards toapply toto xic chemical substances and tobacteria
presenting a health hazard which are present in water intended for
human consumption and the definition of physical,chemical and biolog-
ical parameters corresponding to the different uses of water and,in
particular,to water for human consumption;
Whereas special rules are envisaged for natural mineral waters;
whereas,furthermore,it is necessary to exclude from the scope of this
Directive medicinal waters and certain waters used in the food industry
where such use does not constitute a hazard to public health;
Whereas by Directive75/440/EEC(5),the Council has already laid
down standards for surface water intended for the abstraction of
drinking water;
Whereas the values fixed for certain parameters must be equal to or
lower than a maximum admissible concentration;
Whereas,in the case of softened water intended for human consump-
tion,the values fixed for certain parameters must be equal to or greater
than a required minimum concentration;
Whereas it is desirable that he Member States should take the values
adopted as a‘guide level';
(1)OJ NoC28,9.2.1976,p.27.
(2)OJ NoC131,12.6.1976,p.13.
(3)OJ NoC112,20.12.1973,p.1.
(4)OJ NoC69,11.6.1970,p.1.
(5)OJ NoL194,25.7.1975,p.34.
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Whereas,since the preparation of water for human consumption may
involve the use of certain substances,rules should be drawn up to
govern the use thereof in order to avoid possible harmful effects on
public health due toexcessive quantities o f such substances;
Whereas the Member States should be authorized to make provision,
under certain conditions,for derogations from this Directive,in partic-
ular to take account of certain special situations;
Whereas,in order to check the values of concentrations for the different
parameters,it is necessary topro vide that Member States take the steps
required to ensure regular monitoring of the quality of water intended
for human consumption;
Whereas the reference methods of analysis defined in the Annexes to
this Directive must be speedily adapted toscientific and technical
progress;whereas,in order to facilitate application of the measures
required for this purpose,provision should be made for a procedure
establishing close cooperation between the Member States and the
Commission within a committee responsible for the adaptation to
scientific and technical progress,
HAS ADOPTED THIS DIRECTIVE:
Article1
This Directive concerns standards for water intended for human
consumption.
Article2
For the purposes of this Directive,water intended for human consump-
tion shall mean all water used for that purpose,either in its original state
or after treatment,regardless of origin,
—whether supplied for consumption,or
—whether
—used in a food production undertaking for the manufacture, processing,preservation or marketing of products or substances
intended for human consumption and
—affecting the wholesomeness of the foodstuff in its finished form.
Article3
With regard towater referred toin the seco nd indent o f Article2,
Member States shall apply the values for the toxic and microbiological
parameters listed in Tables D and E respectively of Annex I and the
values for the other parameters which the competent national authorities
consider are likely to affect the wholesomeness of the foodstuff in its
finished form.
Article4
1.This Directive shall not apply to:
(a)natural mineral waters recognized or defined as such by the
competent national authorities;
(b)medicinal waters recognized as such by the competent national
authorities.
2.Member States may not prohibit or impede the marketing of
foodstuffs on grounds relating to the quality of the water used where the
quality of such water meets the requirements of this Directive unless
such marketing constitutes a hazard to public health.
Article5
This Directive shall apply without prejudice to the specific provisions of
other Community regulations.
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Article6
1.Member States shall send the Commission:
—appropriate information as to the industrial sectors in which the competent national authorities consider that the wholesomeness of
the finished product,within the meaning of Article2,is unaffected
by the quality of the water used;
—national values for parameters other than the toxic and microbiolo-gical parameters referred toin Article3.
2.The Commission shall examine this information and shall take any
measures which may be appropriate.It shall periodically draw up a
comprehensive report for the Member States.
Article7
1.Member States shall fix values applicable towater intended fo r
human consumption for the parameters shown in Annex I.
2.Member States may refrain from fixing,pursuant to the first
paragraph,the values of parameters in respect of which no value is
shown in Annex I,as long as these values have not been determined by
the Council.
3.For the parameters given in Tables A,B,C,D,and E of Annex I:
—the values tobe fixed by the Member States must be less than o r the same as the values shown in the‘Maximum admissible concentra-
tion'column;
—in fixing the values,Member States shall take as a basis the values appearing in the‘Guide level'column.
4.For the parameters appearing in Table F of Annex I,the values to
be fixed by Member States must be not lower than those given in the
‘Minimum required concentration'column for softened water,of the
kind referred toin the first indent o f Article2.
5.In the interpretation of the values shown in Annex I account shall
be taken of the observations.
6.Member States shall take the steps necessary toensure that water
intended for human consumption at least meets the requirements speci-
fied in Annex I.
Article8
Member States shall take all the necessary measures toensure that any
substances used in the preparation of water for human consumption do
not remain in concentrations higher than the maximum admissible
concentration relating to these substances in water made available to the
user and,that they do not,either directly or indirectly,constitute a
public health hazard.
Article9
1.Member States may make provision for derogations from this
Directive in order to take account of:
(a)situations arising from the nature and structure of the ground in the
area from which the supply in question emanates.
Where a Member State decides to make such a derogation,it shall
inform the Commission accordingly within two months of its
decision stating the reasons for such derogation;
(b)situations arising from exceptional meteorological conditions.
Where a Member State decides to make such a derogation,it shall
inform the Commission accordingly within15days of its decision
stating the reasons for this derogation and its duration.
2.Member States shall report to the Commission only those deroga-
tio ns referred toin paragraph1which relate toa daily water supply o f
at least1000m3or a population of at least5000.
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3.In no case shall the derogations made by virtue of this Article
relate to toxic or microbiological factors or constitute a public health
hazard.
Article10
1.In the event of emergencies,the competent national authorities
may,for a limited period of time and up to a maximum value to be
determined by them,allow the maximum admissible concentration
shown in Annex I to be exceeded,provided that this does not constitute
an unacceptable risk to public health and provided that the supply of
water for human consumption cannot be maintained in any other way.
2.Without prejudice to the application of Directive75/440/EEC,and
in particular Article4(3)thereof,when,for its supply of drinking
water,a Member State is obliged to resort to surface water which does
not reach the concentrations required of category A3water within the
meaning of Article2of the aforementioned Directive and when it
cannot devise suitable treatment to obtain drinking water of the quality
laid down by this Directive,it may,for a limited period of time and up
toa maximum permissible value which it shall determine,autho rize the
maximum admissible concentration shown in Annex I to be exceeded
provided that this does not constitute an unacceptable risk to public
health.
3.Member States which have recourse to the derogations referred to
in this Article shall immediately inform the Commission thereof,stating
the reasons for and probable duration of such derogations.
Article11
Member States shall ensure that all necessary measures taken toapply
the provisions taken pursuant to this Directive shall in no case have the
effect of allowing,directly or indirectly,either any deterioration in the
present quality of water intended for human consumption or an increase
in the pollution of waters used for the production of drinking water.
Article12
1.Member States shall take all necessary steps toensure regular
monitoring of the quality of water intended for human consumption.
2.All water intended for human consumption shall be monitored at
the point where it is made available to the user in order to check
whether it meets the requirements laid down in Annex I.
3.The points of sampling shall be determined by the competent
national authorities.
4.For such monitoring,Member States shall conform with Annex II.
5.Member States shall as far as practicable use the reference
methods of analysis set out in Annex III.
Laboratories using other methods shall ensure that the results thus
obtained are equivalent to or comparable with the results obtained by
the methods indicated in Annex III.
Article13
Such changes as are necessary for adapting the reference methods of
analysis set out in Annex III to scientific and technical progress shall be
adopted in accordance with the procedure laid down in Article15.
Article14
(a)A Committee on the Adaptation to Scientific and Technical
Progress,hereinafter called‘the Committee',is hereby set up;it
shall consist of representatives of the Member States with a repres-
entative of the Commission as Chairman.
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(b)The Committee shall adopt its own rules of procedure.
Article15
1.Where the procedure laid down in this Article is to be followed,
the matter shall be referred to the Committee by its chairman,either on
his own initiative or at the request of a representative of a Member
State.
2.The representative of the Commission shall submit to the
Committee a draft of the measures to be taken.The Committee shall
give its opinion on that draft within a time limit set by the Chairman
having regard to the urgency of the matter.Opinions shall be adopted
by a majority of?A262?votes,the votes of the Member States
being weighted as in Article148(2)of the Treaty.The
Chairman shall not vote.
3.(a)Where the measures envisaged are in accordance with the
opinion of the Committee,the Commission shall adopt them.
(b)Where the measures envisaged are not in accordance with the
opinion of the Committee,or if no opinion is delivered,the
Commission shall without delay submit to the Council a
proposal on the measures to be taken.The Council shall act by a
qualified majority.
(c)If,within three months of the proposal being submitted to it,the
Council has not acted,the proposed measures shall be adopted
by the Commission.
Article16
Without prejudice to Article4(2),Member States may lay down more
stringent provisions than those provided for in this Directive for water
intended for human consumption.
Article17
Member States may adopt special provisions regarding information—
both on packaging or labels and in advertising—concerning a water’s
suitability for the feeding of infants.Such provisions may also concern
the properties of the water which determine the use of the said informa-
tion.
Member States which intend taking such measures shall inform the
other Member States and the Commission of them beforehand.
▼M2
Article17a
At intervals of three years the Member States shall send information to
the Commission on the implementation of this Directive,in the form of
a sectoral report which shall also cover other pertinent Community
Directives.This report shall be drawn up on the basis of a questionnaire
or outline drafted by the Commission in accordance with the procedure
laid down in Article6of Directive91/692/EEC(1).The questionnaire or
outline shall be sent to the Member States six months before the start of
the period covered by the report.The report shall be sent to the
Commission within nine months of the end of the three-year period
covered by it.
The first report shall cover the period from1993to1995inclusive.
The Commission shall publish a Community report on the implementa-
tion of the Directive within nine months of receiving the reports from
the Member States.
(1)OJ NoL377,31.12.1991,p.48.
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Article18
1.Member States shall bring into force the laws,regulations and
administrative provisions necessary to comply with this Directive and
its Annexes within two years following its notification.They shall
forthwith inform the Commission thereof.
2.Member States shall communicate to the Commission the texts of
the main provisions of national law which they adopt in the field
governed by this Directive.
Article19
The Member States shall take the necessary measures toensure that the
quality of water intended for human consumption complies with this
Directive within five years of its notification.
Article20
Member States may,in exceptional cases and for geographically defined
population groups,submit a special request to the Commission for a
longer period for complying with Annex I.
This request,for which grounds must be duly put forward,shall set out
the difficulties experienced and must propose an action programme with
an appropriate timetable to be undertaken for the improvement of the
quality of water intended for human consumption.
The Commission shall examine these programmes,including the timeta-
bles.In the case of disagreement with the Member State concerned,the
Commission shall submit appropriate proposals to the Council.
Article21
This Directive is addressed tothe Member States.
▼B
Parameters Expression of the
results(1)
Guide
level(GL)
Maximum admi-
ssible concentra-
tion(MAC)
Comments
Parameters Expression of
the results()
Guide level
(GL)
Maximum admi-
ssible concentra-
tion(MAC)
Comments
ANNEX I
LIST OF PARAMETERS
https://www.360docs.net/doc/fd13127649.html,ANOLEPTIC PARAMETERS
1Colour mg/l Pt/Coscale120
2Turbidity mg/l SiO
2
110
Jackson units0·44—Replaced in certain circum-
stances by a transparency
test,with a Secchi disc
reading in meters:
GL:6m
MAC:2m
3Odour Dilution number02at12°C
3at25°C —Tobe related tothe taste tests.
4Taste Dilution number02at12°C
3at25°C —Tobe related tothe o do ur tests.
(1)If,on the basis of Directive71/354/EEC as last amended,a Member State uses in its national legislation,adopted
in accordance with this Directive,units of measurement other than these indicated in this Annex,the values thus indicated must have the same degree of precision.
B.PHYSICO-CHEMICAL PARAMETERS(in relation to the water’s natural structure)
5Temperature°C1225
6Hydrogen
ion concen-
tration pH unit6·5≤pH
≤8·5
—The water should not be
aggressive.
—The pH values dono t apply
towater in clo
sed
containers.
—Maximum admissible value:
9·5.
7ConductivityμS cm?1
at20°C 400—Corresponding to the miner-
alization of the water.
—Corresponding relativity
values in ohms/cm:2500.
8Chlorides Cl mg/l25—Approximate concentration
above which effects might
occur:200mg/l.
9Sulphates SO
4
mg/l25250
10Silica SiO
2
mg/l—See Article8.
11Calcium Ca mg/l100
12Magnesium Mg mg/l3050
Parameters Expression of
the results()
Guide level
(GL)
Maximum admi-
ssible concentra-
tion(MAC)
Comments
Parameters Expression of
the results(1)
Guide level(GL)
Maximum
admissible
concentration
(MAC)
Comments
13Sodium Na mg/l20175
(as from1984
and with a
percentile of90)
150
(as from1987
and with a
percentile of80)
(these percen-
tiles should be
calculated over
a reference
period of three
years)—The values of this parameter take account of the recom-
mendations of a WHO
working party(The Hague,
May1978)on the progres-
sive reduction of the current
total daily salt intake to6g.—As from1January1984the Commission will submit to
the Council reports on
trends in the total daily
intake of salt per popula-
tion.
—In these reports the Commission will examine
towhat extent the120mg/l
MAC suggested by the
WHO working party is
necessary toachieve a satis-
factory total salt intake
level,and,if appropriate,
will suggest a new salt
MAC value tothe Co uncil
and a deadline for compli-
ance with that value.—Before1January1984the Commission will submit to
the Council a report on
whether the reference period
of three years for calcu-
lating these percentiles is
scientifically well founded.
14Potassium K mg/l1012
15Aluminium Al mg/l0·050·2
16Total hard-
ness
—See Table F,page23.
17Dry residues mg/l after
drying at
180°C
1500
18Dissolved
oxygen %O
2
satura-
tion
—Saturation value>75%
except for underground
water.
19Free carbon
dioxide CO
2
mg/l—The water should not be
aggressive.
C.PARAMETERS CONCERNING SUBSTANCES UNDESIRABLE IN EXCESSIVE
AMOUNTS(1)
20Nitrates NO
3
mg/l2550
21Nitrites NO
2
mg/l0·1
22Ammonium NH
4
mg/l0·050·5
23Kjeldahl
Nitrogen
(excluding N in
NO
2and NO
3
)
N mg/l1
Parameters Expression of
the results(1)
Guide level(GL)
admissible
concentration
(MAC)
Comments
24(K Mn O
4)
Oxidizability O
2
mg/l25—Measured when heated
in acid medium.
25Total organic
carbon(TOC)C mg/l—The reason for any
increase in the usual
concentration must be
investigated.
26Hydrogen
sulphide Sμg/l undetectable
organolepti-
cally
27Substances
extractable in
chloroform mg/l dry
residue
0·1
28Dissolved or
emulsified
hydrocarbons
(after extraction
by petroleum
ether);Mineral
oils
μg/l10
29Phenols(phenol
index)C
6
H
5
OH
μg/l
0·5—Excluding natural
phenols which do not
react tochlo rine.
30Boron Bμg/l1000
31Surfactants
(reacting with
methylene blue)μg/l(lauryl
sulphate)
200
32Other organo-
chlorine
compounds not
covered by
parameters No
55μg/l1—Haloform concentrations
must be as low as
possible.
33Iron Feμg/l50200 34Manganese Mnμg/l2050
35Copper Cuμg/l100
—at outlets of
pumping
and/or treat-
ment works
and their
substations —Above3000μg/l astrin-gent tast discolouration
+corrosion may occur.
3000—after the
water has
been
standing for
12hours in
the piping
and at the
point where
the water is
made avail-
able tothe
consumer
36Zinc Znμg/l100
—at outlets of
pumping
and/or treat-
ment works —Above5000μg/l astrin-gent taste,opalescence
and sand-like deposits
may occur.
Parameters Expression of
the results(1)
Guide level(GL)
admissible
concentration
(MAC)
Comments
Parameters Expression of
the results
Guide
level(GL)
Maximum
admissible
concentration
(MAC)
Comments
and their
substations
5000
—after the
water has
been
standing for
12hours in
the piping
and at the
point where
the water is
made avail-
able tothe
consumer
37Phosphorus P
2O
5
μg/l4005000
38Fluoride Fμg/l—MAC varies according
toaverage temperature
in geographical area
concerned.
8—12°C1500
25—30°C700
39Cobalt Coμg/l
40Suspended
solids
None
41Residual
Chlorine
Clμg/l—See Article8.
42Barium Baμg/l100
43Silver Agμg/l10If,exceptionally,silver is
used non-systematically to
process the water,a MAC
value of80μg/l may be
authorized.
(1)Certain of these substances may even be toxic when present in very substantial quantities.
D.PARAMETERS CONCERNING TOXIC SUBSTANCES
44Arsenic Asμg/l50
45Beryllium Beμg/l
46Cadmium Cdμg/l5
47Cyanides CNμg/l50
48Chromium Crμg/l50
49Mercury Hgμg/l1
50Nickel Niμg/l50
Parameters Expression of
the results
Guide
level(GL)
Maximum
admissible
concentration
(MAC)
Comments
Maximum admissible concentration(MAC)
Parameters Results:volume of
the sample in ml
Guide level
(GL)Membrane filter
method
Multiple tube method
(MPN)
51Lead Pbμg/l50
(in running
water)Where lead pipes are present,the lead content should not exceed 50μg/l in a sample taken after flushing.If the sample is taken either directly or after flushing and the lead content either frequently or toan appreciable extent exceeds 100μg/l,suitable measures must be taken toreduce the expo sure to lead on the part of the consumer.
52Antimony Sbμg/l10 53Selenium Seμg/l10 54Vanadium Vμg/l
55Pesticides and
related products μg/l‘Pesticides and related products'
means:
—substances
considered
separately 0·1—insecticides:
—persistent organochlorine
compounds
—organophosphorous
compounds
—carbamates
—total0·5—herbicides
—fungicides
—PCBs and PCTs
56Polycyclic
aromatic hydro-
carbons μg/l0·2?C1—reference substances:
—fluoranthene
—3,4—benzofluoranthene
—11,12—benzofluoranthene
—3,4—benzpyrene
—1,12—benzperylene
—indeno(1,2,3—cd)
pyrene.?
E.MICROBIOLOGICAL PARAMETERS
57Total coli-
forms(1)
100—0MPN<1
58Fecal coliforms100—0MPN<1
59Fecal strepto-
cocci
100—0MPN<1
60Sulphite-
reducing Clos-
tridia
20——MPN≤1
Water intended for human consumption should not contain pathogenic organisms.
If it is necessary to supplement the microbiological analysis of water intended for human consumption,the samples should be examined not only for the bacteria referred to in Table E but also for pathogens including:—salmonella,
—pathogenic staphylococci,
—fecal bacteriophages,
—entero-viruses;
nor should such water contain:
—parasites,
—algas,
—other organisms such as animalcules.
(1)Provided a sufficient number of samples is examined(95%consistent results).
Parameters
Results:
size of
sample(in
ml)
Guide
level(GL)
Maximum
admissible
concentration
(MAC)
Comments
Parameters Expression of the
results
Minimum required
concentration
(softened water)
Comments
61Total bacteria
counts for water
37°C110(1)(2)—
supplied for
human
consumption
22°C1100(1)(2)—
62Total bacteria37°C1520On their own responsibility counts for water
in closed containers 22°C120100
and where parameters57,
58,59and60are complied
with,and where the path-
ogen organisms given on
page22are absent,Member
States may process water
for their internal use the
total bacteria count of which
exceeds the MAC values
laid down for parameter62.
MAC values should be
measured within12hours of
being put intoclo
sed
containers with the sample
water being kept at a
constant temperature during
that12-hour period.
(1)For disinfected water the corresponding values should be considerably lower at the point where it leaves the
processing plant.
(2)If,during successive sampling,any of these values is consistently exceeded a check should be carried out.
F.MINIMUM REQUIRED CONCENTRATION FOR SOFTENED WATER INTENDED FOR
HUMAN COMSUMPTION
1Total hardness mg/l Ca60Calcium or equivalent cations.
2Hydrogen ion
concentration
pH
3Alkalinity mg/l HCO
330The water should not be
aggressive.
4Dissolved oxygen
NB:—The provisions for hardness,hydrogen ion concentration,dissolved oxygen and calcium also apply to desalinated water.
—If,owing to its excessive natural hardness,the water is softened in acordance with Table F before being supplied for consumption,its sodium content may,in exceptional cases,be higher than the values given in the‘Maximum admissible concentration'column.However,an effort must be made to keep the sodium content at as low a level as possible and the essential requirements for the protection of public health may not be disregarded.
▼B
French degree English degree German degree Milligrams of
Ca
Millimoles of
Ca
TABLE OF CORRESPONDENCE BETWEEN THE VARIOUS UNITS OF WATER HARDNESS
MEASUREMENT
French degree10·700·564·0080·1
English degree1·4310·805·730·143 German degree1·791·2517·170·179 Milligrams of Ca0·250·1750·14010·025 Millimoles of Ca1075·640·081
▼B
Volume of Population
concerned
Analysis C1Analysis C2Analysis C3Analysis C4
water produced or distributed in
m3/day (assuming200
l/day per
person)
Number of
samples per
year
Number of
samples per
year
Number of
samples per
year
ANNEX II
PATTERNS AND FREQUENCY OF STANDARD ANALYSES
B.TABLE OF MINIMUM FREQUENCY OF STANDARD ANALYSES(3) 100500(1)(1)(1)Frequency tobe
determined by the
competent national
authorities as the
situation requires
▼B
Volume of Population
concerned
Analysis C1Analysis C2Analysis C3Analysis C4
water produced or distributed in
m3/day (assuming200
l/day per
person)
Number of
samples per
year
Number of
samples per
year
Number of
samples per
year
10005000(1)(1)(1)
200010000123(1)
10000500006061
20000100000120122
30000150000180183
60000300000360(2)366
100000500000360(2)6010
2000001000000360(2)120(2)20(2)
10000005000000360(2)120(2)20(2)
(1)Frequency left to the discretion of the competent national authorities.However,water intended for the food-manu-
facturing industries must be monitored at least once a year.
(2)The competent health authorities should endeavour to increase this frequency as far as their resources allow.
(3)(a)In the case of water which must be disinfected,microbiological analysis should be twice as frequent.
(b)Where analyses are very frequent,it is advisable to take samples at the most regular intervals possible.
(c)Where the values of the results obtained from samples taken during the preceding years are constant and
significantly better than the limits laid down in Annex I,and where no factor likely to cause a deterioration in the quality of the water has been discovered,the minimum frequencies of the analyses referred to above may be reduced:
—for surface waters,by a factor of2with the exception of the frequencies laid down for microbiological analyses;
—for ground waters,by a factor of4,but without prejudice to the provisions of point(a)above.
▼B
ANNEX III
REFERENCE METHODS OF ANALYSIS
https://www.360docs.net/doc/fd13127649.html,ANOLEPTIC PARAMETERS
1Colour Photometric method calibrated on the Pt/co scale.
2Turbidity Silica method—Formazine test—Secchi’s method.
3Odour Successive dilutions,tested at12°C r25°C.
4Taste Successive dilutions,tested at12°C r25°C.
B.PHYSICO-CHEMICAL PARAMETERS
5Temperature Thermometry.
6Hydrogen ion concentration Electrometry.
7Conductivity Electrometry.
8Chlorides Titrimetry—Mohr’s method.
9Sulphates Gravimetry—complexometry—spectrophotometry.
10Silica Absorption spectrophotometry.
11Calcium Atomic absorption—complexometry.
12Magnesium Atomic absorption.
13Sodium Atomic absorption.
14Potassium Atomic absorption.
15Aluminium Atomic absorption—absorption spectrophotometry.
16Total hardness Complexometry.
17Dry residue Dessication at180°C and weighing.
18Dissolved oxygen Winkler’s method—Specific electrode method.
19Free carbon dioxide Acidimetry.
C.PARAMETERS CONCERNING UNDESIRABLE SUBSTANCES
20Nitrates Absorption spectrophotometry—Specific electrode method.
21Nitrites Absorption spectrophotometry.
22Ammonium Absorption spectrophotometry.
23Kjeldahl Nitrogen Oxidation with Titrimetry or Absorption spectrophotometry.
24Oxidizability Boiling for10minutes with KMnO
4
in acid medium.
25Total organic carbon(TOC)—
26Hydrogen sulphide Absorption spectrophotometry.
27Substances extractable in chloroform Liquid/liquid extraction using purified chloroform at neutral pH,weighing the residue.
28Hydrocarbons(dissolved or in
emulsion);Mineral oils
Infra-red absorption spectrophotometry.
29Phenols(phenol index)Absorption spectrophotometry,paranitroaniline method and4-
aminoantipyrine method.
30Boron Atomic absorption—Absorption spectrophotometry.
31Surfactants(reacting with
metylene blue)
Absorption spectrophotometry with methylene blue.
32Other organo-chlorine compounds Gas-phase or liquid-phase chromatography after extraction by appropriate solvents and purification—Identification of the constituents of mixtures if necessary.Quantitative deter-mination.
33Iron Atomic absorption—Absorption spectrophotometry.
34Manganese Atomic absorption—Absorption spectrophotometry.
35Copper Atomic absorption—Absorption spectrophotometry.
36Zinc Atomic absorption—Absorption spectrophotometry.
37Phosphorus Absorption spectrophotometry.
38Fluoride Absorption spectrophotometry—Specific electrode method.
39Cobalt—
40Suspended solids Method of filtration on toμ0·45porous membrane or centri-
fuging(for at least15minutes with an average acceleration of
2800to3200g)dried at105°C and weighed.
41Residual chlorine Titrimetry—Absorption spectrophotometry.
42Barium Atomic absorption.
D.PARAMETERS CONCERNING TOXIC SUBSTANCES
43Silver Atomic absorption.
44Arsenic Absorption spectrophotometry—Atomic absorption.
45Beryllium—
46Cadmium Atomic absorption.
47Cyanides Absorption spectrophotometry.
48Chromium Atomic absorption—Absorption spectrophotometry.
49Mercury Atomic absorption.
50Nickel Atomic absorption.
51Lead Atomic absorption.
52Antimony Absorption spectrophotometry.
53Selenium Atomic absorption.
54Vanadium—
55Pesticides and related products See method32.
56Polycyclic aromatic hydrocar-bons Measurement of intensity of fluorescence ultraviolet after extraction using hexane—gas-phase chromatography or measurement in ultraviolet after thin layer chromatography—Comparative measurements against a mixture of six standard substances of the same concentration(1).
(1)?C1Standard substances to be considered:fluoranthene,
3,4—benzofluoranthene,11,12—benzofluoranthene,
3,4—benzpyrene,1,12—benzperylene,indeno(1,2,3—cd)pyrene.?
E.MICROBIOLOGICAL PARAMETERS
Fermentation in mutliple tubes.Subculturing of the positive
tubes on a confirmation medium.Count according to MPN
(most probable number)
57(2)Total coliforms or
58(2)Fecal coliforms Membrane filtration and culture on an appropriate medium
such as Tergitol lactose agar,endo agar,0·4%Teepol broth,
subculturing and identification of the suspect colonies—
Incubation temperature for total coliforms:37°C
Incubation temperature for fecal coliforms:44°C
59(2)Fecal streptococci Sodium azide method(Litsky).Count according to MPN—
Membrane filtration and culture on an appropriate medium. 60(2)Sulphitereducing Clostridia A spore count,after heating the sample to80°C by:
—seeding in a medium with glucose,sulphite and iron,
counting the black-halo colonies;
—membrane filtration,deposition of the inverted filter on a
medium with glucose,sulphite and iron covered with agar,
count of black colonies;
—distribution in tubes of differential reinforced clostridial
medium(DRCM),subculturing of the black tubes in a
medium of litmus-treated milk,count according to MPN. 61/62(2)Total counts Inoculation by placing in nutritive agar.
ADDITIONAL TESTS
Salmonella Concentration by membrane filtration.Inoculation on a pre-
enriched medium.Enrichment,subculturing on isolating agar.
Identification.
Pathogenic staphylococci Membrane filtration and culture on a specific medium(e.g.
Chapman’s hypersaline medium).Test for pathogenic charac-
teristics.
Fecal bacteriophages Guelin’s process.
Enteroviruses Concentration by filtration,flocculation or centrifuging,and
identification.
Protozoa Concentration by filtration on a membrane,microscopic exam-
ination,test for pathogenicity.
Animalcules(worms—larvae)Concentration by filtration on a membrane.Microscopic
examination.Test for pathogenicity.
(2)Comments:The incubation period is generally24or48hours except for total counts,when it is48or72hours.
F.MINIMUM REQUIRED CONCENTRATION
Alkalinity Acidimetry with Methyl orange
中国美国日本欧盟四国饮用水质标准比较
. 快适水水质卫生标准 1、快适水概念 水质指标达到美国、欧盟、日本和中国现行饮用水标准中最高要求,适合于婴幼儿等对水中污染物较为敏感的人群长期饮用的优质饮用水。 2、美国、日本、欧盟和中国四国或地区饮用水水质标准比较 2.1分类的区别 (1)美国水质标准分为国家一级饮用水水质标准和二级饮用水标准。国家一级饮用水水质标准中又有最大污染物浓度(MCL)和最大污染物浓度目标(MCLG)两个指标,MCL为强制性的标准,MCLG是非强制性的更高目标值。美国一级饮用水指标共有78个,分为:无机物、有机物、放射性物质、微生物学指标,其中无机物指标有15个,有机物指标54个,放射性物质指标有3个,微生物学指标有6个;二级饮用水污染物指标共有15个,没有细分。 (2)欧盟水质标准并没有特别分类,水质指标分为微生物学指标、化学物质指标和指示指标,其中微生物学指标2个(瓶桶装水是5个),化学物质指标26个,指示指标20个。 (3)日本水质标准分为水质基准项目和水质管理目标设定项目。水质指标项目分为病原微生物、重金属、无机物、金属类、有机物、消毒剂残留及消毒副生成物、基本特性、其他类。日本水质基准项目共50个,其中病原微生物指标有2个,重金属指标有10个,无机物指标有9个,有机物指标有11个,消毒剂和消毒副生成物10个,基本特性指标5个,其他类指标2个;水质管理目标设定项目共27个,其中重金属和金属指标有4个,无机物指标有2个,有机物指标有9个,消毒剂和消毒副生成物6个,其他类6个。 (4)中国生活饮用水卫生标准GB5749分为水质常规指标及限值、饮用水中消毒剂常规指标及要求、水质非常规指标及限值,共计106项。饮用水标准水质常规指标分为微生物指标、毒理指标、感官性状和一般化学指标、放射性指标四类共1 / 19 . 38个,其中微生物指标有4个,毒理指标有15个,感官性状和一般化学指标有17个,放射性指标2个;饮用水中消毒剂常规指标4个;水质非常规指标及限值分为微生物指标2个、毒理指标59个、感官性状和一般化学指标3个。 2.2水质指标对比 以中国生活饮用水卫生标准GB5749中水质常规指标及限值、水质非常规指标及限值为参照,中国、美国、日本和欧盟4个国家和地区的水质指标对比见表1和表2。 表1 水质常规指标及限值对比 限指中美日欧 GB5749-20MC6MCL标 、微生物指 总大肠菌51MPN/100m不得检CFU/100m 耐热大肠菌群MPN/100m不得检 CFU/100m
解读《生活饮用水卫生标准》(GB5749-2006)
解读《生活饮用水卫生标准》(GB5749-2006) 点题 《生活饮用水卫生标准》(GB 5749-2006)已于2006年12月29日由国家标准委和卫生部联合发布。同时发布的还有13项生活饮用水卫生检验方法国家标准。这些标准将于今年7 月1日起开始实施。 《生活饮用水卫生标准》首次发布于1985年,已实施了20年,本次为第一次修订。经过修订,标准中的指标数量不仅由35项增至106项,还对原标准的8项指标进行了修订,指标限量也与发达国家的饮用水标准具有可比性。 生活饮用水对百姓健康安全非常重要,饮用水一旦出了问题,就会给百姓生活带来重大影响。这是一项必将对百姓生活和社会产生重大影响的国家标准。本篇文章对该标准中经过修订的各项指标进行全面解析,以加深广大读者对该标准的认识。 指标大有来头危害各不相同 《生活饮用水卫生标准》中106项指标包括微生物指标6项,毒理指标74项(其中,无机化合物指标21项,有机化合物指标53项),感官性状和一般化学指标20项,消毒剂指标4项,放射性指标2项。各类指标中,可能对人体健康产生危害或潜在威胁的指标占80%左右,属于影响水质感官性状和一般理化指标即不直接影响人体健康的指标约占20%。 可能对生活饮用水卫生安全造成影响的物质究竟从何而来?据标准主要起草人、中国疾病预防控制中心环境与健康相关产品安全所研究员鄂学礼介绍,污染生活饮用水的微生物主要来自水源地的人畜粪便,还有医院排放的污水以及腐烂的动物尸体等。微生物指标超标,很容易引发传染性肠道疾病,包括世界卫生组织和很多国家的饮用水卫生标准,都将微生物指标放在第一位。我国原生活饮用水卫生标准中的微生物指标只有总大肠菌群和菌落总数两项指标,新标准中增加的耐热大肠菌群(粪大肠菌群)和大肠埃希氏菌两项指标,均属于对总大肠菌群指标的细化,如果按照标准规定的发酵法检出这两种微生物或按照滤膜法监测超出限值,就说明生活饮用水受到微生物的污染。以上4项微生物指标都属于常规检验指标,还有两种原虫即贾第鞭毛虫和隐孢子虫,同属于微生物指标,列入新标准的非常规检验项目,国外突发性肠道传染病的相关报道中,很多都是由这两种原虫引发的。但微生物污染比较容易检出,也比较容易消除,只要按照相关规程操作,绝大部分水站都可 以做到。 原标准的毒理指标只有15项,新标准的毒理指标几乎是原标准的5倍,达到74项。其中的有机化合物指标由5项增至53项,无机化合物指标由10项增至21项。这些化合物的主要来源是农药和工业污染,我国不少地方的水源地农药污染比较严重,虽然如六六六、滴滴涕、乐果等农药已被禁止使用,但早些年使用过的这些农药仍残留在土壤中,短时间内
农村实施《生活饮用水卫生标准》准则
农村实施《生活饮用水卫生标准》准则 1991年5月3日,全国爱卫会、卫生部 一.总则 1.为保证居民生活饮用水水质符合安全卫生,逐步达到国家《生活饮用水卫生标准》的要求,保护人民的身体健康,促进农村改水事业的发展,特制定本准则。 2.本准则适用于广大农村居民点的集中式给水和分散式给水。 3.在新建或改建集中式给水时,对水源选择、水源防护和工程设计要符合本准则及有关标准、法令的要求,事先认真审查设计,事后组织竣工验收,经卫生行政部门同意后,方可投入使用。供水单位必须保证水质符合本准则的要求。 4.分散式给水的水源选择、水质鉴定、水源卫生防护和经常管理工作,由供水所在地的乡、镇政府委托当地有关单位管理。 二.水质分级评价准则和卫生要求 1.农村生活饮用水水质不得超过下表所规定的限值。(见下页) 2.集中式给水除根据需要具备必要的净水设施外,必须进行消毒,保证正常运转,并建立健全管理制度和操作规程,以保证供水质量。 3.农村给水的水质应达到二级以上,但是,在特殊情况下,如水源选择和处理条件受限制的地区,容许按三级水质要求处理。 4.二级、三级水质要求主要是考虑某些地区由于经济、地理等因素所致的水源选择和处理条件受到限制的情况,对某些指标适当放宽了要求。但是,决不准以二、三级水的要求做为借口,放松对“三废”的排放要求,使污染水源、恶化水质的行为合法化。
三.水源选择、水源卫生防护及本准则未做明确规定的其它卫生要求,参照现行的《生活饮用水卫生标准》(GB5749—85)和《农村生活饮用水量卫生要求》(GB11730—89)有关规定执行。 生活饮用水水质分级要求 ---------------------------------------项目一级二级三级 ---------------------------------------感官性状和一般化学指标: 色(度)15,并不呈现其它异色20 30 浑浊度(度3,特殊情况不超过5 10 20 肉眼可见物不得含有不得含有不得含有PH 6.5~8.5 6~9 6~9 总硬度(ml/L以碳酸钙计)450 550 700 铁(ml/L)0.3 0.5 1.0 锰(ml/L)0.1 0.3 0.5 氯化物(ml/L)250 300 450 硫酸盐(ml/L)250 300 400 溶解性总固体(ml/L)1000 1500 2000 毒理学指标: 氟化物(ml/L) 1.0 1.2 1.3 砷(ml/L)0.05 0.05 0.05 汞(ml/L)0.001 0.001 0.001 镉(ml//L)0.01 0.01 0.01 铬(六价)(ml/L)0.05 0.05 0.05 铅(ml/L)0.05 0.05 0.05 硝酸盐(ml/L以氮计)20 20 20 细菌学指标: 细菌总数(个/ml)100 200 500 总大肠菌群(个/L) 3 11 27 (接触30分钟后)游离余氯(ml/L)0.3 不低于0.3 不低于0.3 出厂水不低于0.05 不低于0.05 末梢水不低于不低于0.05 ---------------------------------------○1一级:期望值;二级:允许值;三级:缺乏其它可选择水源时的放宽限值。 四.水质检查:应参照现行《生活饮用水卫生标准》和《生活饮用水标准检验方法》(GB5750—85)中有关规定执行。
欧盟饮用水水质指令
《欧盟饮用水水质指令》 A.微生物学参数 以下指标用于瓶装或桶装饮用水: B.化学物质参数
注:1.参数值是指水中的剩余单体浓度,并根据相应聚合体与水接触后所能释放出的最大量计算得; 2.如果可能,在不影响消毒效果的前提下,成员国应尽力降低该值. 3.该值适用于由用户水嘴处所取水样,且水样应能代表用户一周用水的平均水质.成员国必须考虑到可能会影响人体健康的峰值出现情况. 4.该指令生效后5-15年,铅的参数值为25μg/L. 5.成员国应确保[硝酸根浓度]/50+[亚硝酸根浓度]/3≤1,方括号中为以mg/L为单位计的硝酸根和亚硝酸根浓度,且出厂水亚硝酸盐含量要小于0.1mg/L. 6.农药是指:有机杀虫剂、有机除草剂、有机杀菌剂、有机杀线虫剂、有机杀螨剂、有机除藻剂、有机杀鼠剂、有机杀粘菌和相关产品及其代谢副产物、降解和反应产物. 7.参数值适用于每种农药.对艾氏剂、狄氏剂、七氯和环氧七氯,参数值为0.030μg/L. 8.农药总量是指所有能检测出和定量的单项农药的总和。 9.具体的化合物包括:苯并[b]呋喃、苯并[k]呋喃、苯并[g,h,i]芘、茚并[1,2,,-cd]芘 10.如果可能,在不影响消毒效果的前提下,成员国应尽力降低下列化合物值:氯仿、溴仿、二溴一氯甲烷和一溴二氯甲烷该指令生效后5-15年,总三卤甲烷的参数值为150μg/L. C.指示参数
注:1.不应具有腐蚀性。 2.如果原水不是来自地表水或没有受地表水影响,则不需要测定该参数。 3.若为瓶装或桶装的静止水,最小值可降至 4.5pH单位,若为瓶装或桶装水,因其天然 富含或人工充入二氧化碳,最小值可降至更低。 4.如果测定TOC参数值,则不需要测定该值。 5.对瓶装或桶装的水,单位为个/250mL。 6.对于供水量小于是10000m3/d的水厂,不需要测定该值。 7.对地表水处理厂,成员国应尽力保证出厂水的浊度不超过1.0NTU。 注:译自Council Directive 98/83/EC on the Quality of Water Intended for Human Consumption
农村实施《生活饮用水卫生标准》准则
农村实施《生活饮用水卫生标准》准则 颁布单位: 全国爱卫会/卫生部颁布日期:1991年5月3日 实施日期:1991年5月3日 1 总则 1.1 为保证居民生活饮用水水质符合安全卫生,逐步达到国家《生活饮用水卫生标准》的要求,保护人民的身体健康,促进农村改水事业的发展,特制定本准则。 1.2本准则适用于广大农村居民点的集中式给水和分散式给水。 1.3在新建或改建集中式给水时,对水源选择、水源防护和工程设计要符合本准则及有关标准、法令的要求,事先认真审查设计,事后组织竣工验收,经卫生行政部门同意后,方可投入使用。供水单位必须保证水质符合本准则的要求。 1.4分散式给水的水源选择、水质鉴定、水源卫生防护和经常管理工作,由供水所在地的乡、镇政府委托当地有关单位管理。 2 水质分级评价准则和卫生要求 2.1农村生活饮用水水质不得超过下表所规定的限值。 生活饮用水水质分级要求
正常运转,并建立健全管理制度和操作规程,以保证供水质量。 2.3农村给水的水质应达到二级以上,但是,在特殊情况下,如水源选择和处理条件受限制的地区,容许按三级水质要求处理。 2.4二级、三级水质要求主要是考虑某些地区由于经济、地理等因素所致的水源选择和处理条件受到限制的情况,对某些指标适当放宽了要求。但是,决不准以二、三级水的要求做为借口,放松对“三废”的排放要求,使污染水源、恶化水质的行为合法化。 3 水源选择、水源卫生防护及本准则未做明确规定的其它卫生要求,参照现行的《生活饮用水卫生标准》(GB5749—85)和《农村生活饮用水量卫生要求》(GB11730—89)有关规定执行。 4 水质检查:应参照现行《生活饮用水卫生标准》和《生活饮用水标准检验方法》(GB5750—85)中有关规定执行。
欧盟饮水指令规定的水质指标及其限值
欧盟饮水指令规定的水质指标及其限值指标限值如下: 微生物指标 大肠杆菌0/100ml 肠球菌0/100ml 市售瓶装水要求 大肠杆菌0/250ml 假单胞菌0/250ml 菌落计数(22℃) 0/250ml 菌落计数(37℃) 100ml 化学指标 丙烯酰胺0.10μg/L 锑 5.0μg/L 砷10μg/L 苯 1.0μg/L 苯并[α] 0.010μg/L 硼 1.0μg/L 溴酸盐10μg/L (最迟于指令实施后10年达到) 25μg/L (指令实施后5~10年的限值) 镉 5.0μg/L 铬50μg/L 铜 2.0mg/L 氰化物50μg/L 1,2-二氯乙烷3.0μg/L 表氯醇0.10μg/L 氟化物 1.5mg/L 铅50μg/L(目前) 25μg/L (指令实施后5~15年的限值) 10μg/L (最迟于指令实施后15年达到) 汞 1.0μg/L 镍20μg/L 硝酸盐50mg/L 亚硝酸盐0.50mg/L 农药①0.10μg/L(单个农药) 农药总量0.50μg/L 多环芳烃②0.10μg/L(特定化合物总浓度) 硒10μg/L 四氯乙烯和三氯乙烯 1.0μg/L(总浓度)
三卤乙烷总量100μg/L(特定化合物总浓度) 氯乙烯0.5μg/L 指标性指标 铝200μg/L 氨0.50μg/L 氯化物③250mg/L 产气荚腊梭状芽孢杆菌(包括芽孢) 0/100ml 色饮用者可以接受,无异常变化 电导率250μS·cm-1(20℃) 氢离子浓度 6.5≤pH值≤9.5 铁200μg/L 锰50μg/L 嗅饮用者可以接受,无异常变化 氧化性 5.0mg/L(O2) 硫酸盐250mg/L 钠200mg/L 味饮用者可以接受,无异常变化 菌落计数(22℃) 无异常变化 大肠杆菌0/100ml 总有机碳无异常变化 浑浊度饮用者可以接受,无异常变化 放射性指标 氚100Bq/L 总指标性计量 (Total indicative dose) 0.10Sv/a ①该值用于单个农药,当农药为艾氏剂、狄氏剂、七氯、七环氧化物时限值为0.030μg/L。 ②②包括苯并荧蒽、苯并[k]荧蒽、苯并[g,h,i]芘和茚并[1,2,3cd]芘。 ③③包括氯仿、溴仿、二溴一氯甲烷和一溴二氯甲烷。
生活饮用水水质标准(最新)..
生活饮用水水质标准(最新)..
生活饮用水水质标准(最新) 文章出处:网责任编辑:作者:人气:101834发表时间:2013-08-26 10:50:00 前言 本标准全文强制。 本标准自实施之日起代替GB5749-85《生活饮用水卫生标准》。 本标准与GB5749-85相比主要变化如下: ——水质指标由GB 5749-85的35项增加至106项,增加了71项;修订了8项;其中: ——微生物指标由2项增至6项,增加了大肠埃希氏菌、耐热大肠菌群、贾第鞭毛虫和隐孢子虫;修订了总大肠菌群; ——饮用水消毒剂由1项增至4项,增加了一氯胺、臭氧、二氧化氯; ——毒理指标中无机化合物由10项增至21项,增加了溴酸盐、亚氯酸盐、氯酸盐、锑、钡、铍、硼、钼、镍、铊、氯化氰;并修订了砷、镉、铅、硝酸盐; 毒理指标中有机化合物由5项增至53项,增加了甲醛、三卤甲烷、二氯甲烷、1,2-二氯乙烷、1,1,1-三氯乙烷、三溴甲烷、一氯二溴甲烷、二氯一溴甲烷、环氧氯丙烷、氯乙烯、1,1-二氯乙烯、1,2-二氯乙烯、三氯乙烯、四氯乙烯、六氯丁二烯、二氯乙酸、三氯乙酸、三氯乙醛、苯、甲苯、二甲苯、乙苯、苯乙烯、2,4,6-三氯酚、氯苯、1,2-二氯苯、1,4-二氯苯、三氯苯、邻苯二甲酸二(2-乙基己基)酯、丙烯酰胺、微囊藻毒素-LR、灭草松、百菌清、溴氰菊酯、乐果、2,4-滴、七氯、六氯苯、林丹、马拉硫磷、对硫磷、甲基对硫磷、五氯酚、莠去津、呋喃丹、毒死蜱、敌敌畏、草甘膦;修订了四氯化碳; ——感官性状和一般理化指标由15项增至20项,增加了耗氧量、氨氮、硫化物、钠、铝;修订了浑浊度; ——放射性指标中修订了总α放射性。 ——删除了水源选择和水源卫生防护两部分内容。 ——简化了供水部门的水质检测规定,部分内容列入《生活饮用水集中式供水单位卫生规范》。 ——增加了附录A。 ——增加了参考文献。 本标准的附录A为资料性附录。 为准备水质净化和水质检验条件,贾第鞭毛虫、隐孢子虫、三卤甲烷、微囊藻毒素-LR等4项指标延至2008年7月1日起执行。 本标准由中华人民共和国卫生部提出并归口 本标准负责起草单位:中国疾病预防控制中心环境与健康相关产品安全所 本标准参加起草单位:广东省卫生监督所、浙江省卫生监督所、江苏省疾病预防控制中心、 北京市疾病预防控制中心、上海市疾病预防控制中心、中国城镇供 水排水协会、中国水利水电科学研究院、国家环境保护总局环境标 准研究所。 本标准主要起草人:金银龙、鄂学礼、陈昌杰、陈西平、张岚、陈亚妍、蔡祖根、甘日华、 申屠杭、郭常义、魏建荣、宁瑞珠、刘文朝、胡林林。
《生活饮用水卫生标准》(GB5749-2006)
《生活饮用水卫生标准》(GB 5749-2006) 随着经济的发展,人口的增加,不少地区水源短缺,有的城市饮用水水源污染严重,居民生活饮用水安全受到威胁。1985年发布的《生活饮用水卫生标准》(GB5749-85)已不能满足保障人民群众健康的需要。为此,卫生部和国家标准化管理委员会对原有标准进行了修订,联合发布新的强制性国家《生活饮用水卫生标准》(GB5749-2006)(下称“新标准”)。 2007年7月1日,由国家标准委和卫生部联合发布的《生活饮用水卫生标准》(GB 5749-2006)强制性国家标准和13项生活饮用水卫生检验国家标准将正式实施。这是国家21年来首次对1985年发布的《生活饮用水标准》进行修订。 《生活饮用水卫生标准》的修订是保证饮用水安全的重要措施之一。在国家标准化管理委员会协调下,由卫生部牵头,会同建设部、国土资源部、水利部、国家环保总局,组织卫生、供水、环保、水利、水资源等各方面专家共同参与完成了该项标准的修订工作。 新标准具有以下三个特点:一是加强了对水质有机物、微生物和水质消毒等方面的要求。新标准中的饮用水水质指标由原标准的35项增至106项,增加了71项。其中,微生物指标由2项增至6项;饮用水消毒剂指标由1 项增至4项;毒理指标中无机化合物由10项增至21项;毒理指标中有机化合物由5项增至53项;感官性状和一般理化指标由15项增至20项;放射性指标仍为2项。二是统一了城镇和农村饮用水卫生标准。三是实现饮用水标准与国际接轨。新标准水质项目和指标值的选择,充分考虑了我国实际情况,并参考了世界卫生组织的《饮用水水质准则》,参考了欧盟、美国、俄罗斯和日本等国饮用水标准。 1985年出台的《生活饮用水卫生标准》里,饮用水浑浊度的指标是“3-5”,新《标准》则将之提高到“1-3”,也就是说,抛开一大堆老百姓看不懂的理化指标不说,最直观能感受到的,是水色将更为清亮。
中国与美国、欧盟生活饮用水水质标准的特点对比
中国与美国、欧盟生活饮用水水质标准的特点对比 从上表可见,在标准的制定时间上,我国较美国晚了45年。自20世纪60年代至今,美国修订标准至少10次,而我国仅修订过2次。美国制定了有关生活饮用水水质标准的相应技术法规,而我国目前尚缺少相关技术法规。 在水质指标数量方面,美国共52项,而我国只有35项,约为美国的67%,因此,在水质监测方面有可能遗漏对某些有害成分的检测项目。在我国水质标准中,有机物指标仅有7项,绝大多数为无机物,其中以重金属离子为主;而美国标准则以有机物为主,多达27项,约占总数的52%。可见中、美两国生活饮用水水质标准的指标监测重点不同。此外,我国生活饮用水水质标准指标要求很低,甚至还有一项肉眼可见物指标。 与欧盟相比,我国的指标分类与其基本一致,而且在性质上都是以无机物指标为主。在指标数量方面,欧盟共56项,比我国多60%,可见其水质监测比我国全面得多
2006年生活饮用水水质标准与85年的相比有什么区别呢? 水质标准由35项增加至106项,增加了71项,修订了8项,其中: 1.微生物指标由2项增至6项,增加了大肠埃希氏菌、耐热大肠菌群、贾第鞭毛虫和隐孢子 虫,修订了总大肠菌群; 2.饮用水消毒剂由1项增至4项,增加了一氯胺、臭氧、二氧化氯; 3.毒理指标中无机化合物由10项增至21项,增加了溴酸盐、亚氯酸盐、氯酸盐、锑、钡、 铍、硼、钼、镍、铊、氯化氰,并修订了砷、镉、铅硝酸盐; 毒理指标中有机化合物由5项增至53项,增加了甲醛、三卤甲烷、二氯甲烷、1,2-二氯乙烷、1,1,1-三氯乙烷、三溴甲烷、一氯二溴甲烷、二氯一溴甲烷、环氧氯丙烷、氯乙烯、1,1-二氯乙烯、1,2-二氯乙烯、三氯乙烯、四氯乙烯、六氯丁二烯、二氯乙酸、三氯乙酸、三氯乙醛、苯、甲苯、二甲苯、乙苯、苯乙烯、2,4,6-三氯酚、氯苯、1,2-二氯苯、1,4-二氯苯、三氯苯、邻苯二甲酸二(2-乙基己基)酯、丙烯酰胺、微囊藻毒素-LR、灭草松、百菌清、溴氰菊酯、乐果、2,4-滴、七氯、六氯苯、林丹、马拉硫磷、对硫磷、甲基对硫磷、五氯酚、莠去津、呋喃丹、毒死蜱、敌敌畏、草甘瞵;修订了四氯化碳; 4.感官性状和一般化学指标由15项增至20项,增加了耗氧量、氨氮、硫化物、钠、铝;修 订了浑浊度; 5.放射性指标中修订了总α放射性。
[Word]欧盟水质检测标准
[Word]欧盟水质检测标准 指标值(个/mL) 指标 埃希氏大肠杆菌 0 肠道球菌 0 以下指标用于瓶装或桶装饮用水: 指标指标值 埃希氏大肠杆菌 0/250mL 肠道球菌 0/250mL 铜绿假单胞菌 0/250mL 细菌总数(22?) 100/mL 细菌总数(37?) 20mL B.化学物质参数 指标指标值单位备注丙烯酰胺0.10 μg/L 锑 5.0 μg/L 砷10 μg/L 苯1.0 μg/L 苯并[a]芘0.010 μg/L 硼 1.0 μg/L 溴酸盐10 μg/L 镉 5.0 μg/L 铬50 μg/L 铜 2.0 μg/L 氰化物50 μg/L 1,2-二氯乙烷3.0 μg/L 环氧氯丙烷0.10 μg/L 氟化物1.5 μg/L 铅10 μg/L 汞 1.0 μg/L 镍20 μg/L 硝酸盐50 μg/L 亚硝酸盐0.50 μg/L 农药0.10 μg/L 农药(总) 0.50 μg/L 多环芳烃0.10 μg/L 硒10 μg/L 四氯乙烯和三氯乙10 μg/L 烯
三卤甲烷(总) 100 μg/L 氯乙烯0.50 μg/L 注:1.参数值是指水中的剩余单体浓度,并根据相应聚合体与水接触后所能释放出的最大量 计算而得;
2.如果可能,在不影响消毒效果的前提下,成员国应尽力降低该值。 3.该值适用于由用户水嘴处所取水样,且水样应能代表用户一周用水的平均水质。成员国必 须考虑到可能会影响人体健康的峰值出现情况。 4.该指令生效后5~15年,铅的参数值为25μg/L。在达到指令中中规定的参数值前,成员 国应确保采用适当的方法,尽可能降低水中铅的浓度。 5.成员国应确保[硝酸盐浓度]/50+[亚硝酸盐浓度]/3?1,方括号中为以mg/L单位计的硝酸盐和亚硝酸盐浓度,且出厂水亚硝酸盐含量要小于0.1mg/L。 6.农药是指:有机杀虫剂、有机除草剂、有机杀菌剂、有机杀线虫剂、有机杀粘菌剂和相关产品及其代谢副产物、降解和反应产物。 7.参数值适用于每种农药。对艾氏剂、狄氏剂、七氯和环氧七氯,参数值为0.030μg/L。 8.农药总量是指所有能检测出和定量的单项农药的总和。 9.具体的化合物包括,苯并荧蒽、苯并[k]荧蒽、苯并[g,h,i]苝,茚并按[1,2,3,-c, d]芘。 10.如果可能,在不影响消毒效果的前提下,成员国应尽力降低下列化合物值:氯仿、溴仿、 二溴一氯甲烷和一溴二氯甲烷该指令生效后5~15年,总三卤甲烷的参数值为150μg/L。 C.指示参数 指标指导值单位备注 用户可以接受且无色度异味 用户可以接受且无浊度注7 异味
中日饮用水标准对比
中日生活饮用水水质标准比较 (刘晓茹李贵宝李文奇) 刘晓茹李贵宝李文奇 摘要:本文比较了中国《生活饮用水水质卫生规范》和日本《生活饮用水水质标准》各自的特点,以及二者在水质指标分类、指标数目和指标值等方面的异同。中国《规范》基本上符合国情,且与国际接轨。 关键词:生活饮用水;标准;日本;比较 自来水是城市人民生活所必需的基本物品,它应是安全、无害,并且清洁卫生、无嗅无味、可口好喝的。“饮用水水质标准”就是为达到此目的而制定的。随着人们生活水平越来越高以及科学技术的日益发展,水质标准也在不断修改与完善。 我国加入WTO后,水环境监测也必须逐渐与国际接轨。2001年中国国家卫生部发布了《生活饮用水卫生规范》(以下简称中国《规范》),该规范从2001年9月1日起实施。《规范》的水质卫生部分,在检测项目和指标值方面都有较大变化,与国际同类标准比较,基本上是一个符合国情又与国际接轨的生活饮用水水质卫生规范。 日本作为中国的邻国,又是经济高度发展的国家,其《生活饮用水水质标准》(以下简称日本《标准》)的制订同时参考了世界卫生组织(WHO)、欧盟(EC)和美国环保局(USEPA)的相关标准,并进行了多次修订。 本文就这两个规范和标准进行对比,以反映中日两国在标准制定方面的差异,促使我国进一步加强对饮用水水质卫生的监督检查工作。 1 中国《生活饮用水卫生规范》概述 1.1 中国《生活饮用水卫生规范》的发展 上海是我国最早制定地方性饮用水标准的城市之一,“上海市饮用水清洁标准”于1928年10月修订公布。1950年上海市人民政府颁布了《上海市自来水水质标准》,共有16项指标。 1954年我国卫生部拟订了一个自来水水质暂行标准草案,有16项指标,于1955年5月在北京、天津、上海等十二个大城市试行,这是新中国成立后最早的一部管理生活饮用水的技术法规。1959年经国家建设部和卫生部批准,定名为《生活饮用水卫生规程》。1976年国家卫生部组织制定了我国第一个国家饮用水标准,共有23项指标,定名为《生活饮用水卫生标准》(编号为TJ 20-
农村饮水安全的标准
农村饮水安全的标准 ? ? 大红花裤衩子 ? 10位粉丝 ? 1楼 农村饮用水安全是关系农村居民生活质量和生命安全的大问题。农村饮用水安全具有公共性,需要政府进行管理。我国农村饮用水安全问题主要体现在水质差、水量不足、取水不便、不能保证供给等方面。为此,需要政府投入和民间筹资多方支持,同时政府应加大宣传力度,加强农村配套设施建设,以消除农村饮用水存在的安全问题和隐患。 水是生命之源。但是随着社会发展,这句话应该改为“安全的水是生命之源”。特别是饮用水安全,已成为政府、社会、公众日益关注的焦点。没有安全的饮用水,就没有健康的生命,更没有和谐的小康社会和社会主义新农村。 什么是农村饮用水安全 什么是安全的水?不同国家的政府制定着不同的安全饮用水标准,同一个国家政府制定的安全饮用水标准也会随着社会经济的发展而变化。 《1998年世界发展指标》认为,安全的水是指经过处理的地表水和未经处理但未被污染的水,如泉水、安全的井水和得到保护的钻孔水。在城市地区,水资源可以是公共取水处,或取水距离不超过2C¨。米的储水管。在农村地区,安全的水意味着家庭成员不必为取水而每天花费过多的时间。足够数量安全的水是指能够满足新陈代谢、卫生和家庭需要的量,通常为每人每天20升。 我国制定的农村饮用水安全卫生评价指标体系将农村饮用水安全分为安全和基本安全两个档次,由水质、水量、方便程度和保证率四项指标组成。四项指标中只要有一项低于安全或基本安全最低值,就不能定为饮用水安全或基本安全。 水质:符合国家《生活饮用水卫生标准》要求的为安全;符合《农村实施<生活饮用水卫生标准>准则》要求的为基本安全。低于《农村实施<生活饮用水卫生标准>准则》要求的为不安全。目前,我国对于农村饮用水不安全主要从氟超标、砷超标、苦咸水、污染水等几个方面来判断。 水量:每人每天可获得的水量不低于40~60升的为安全,不低于20~40升的为基本安全。常年水量不足的,属于农村饮用水不安全。在我国,根据气候特点、地形、水资源条件和生活习惯,将全国划分为5个类型区,不同地区的安全饮用水量标准有所不同。安全饮用水水量标准从一区到五区分别是每人每天40升、45升、50升、55升、60升。基本安全饮用水水量标准从~区到五区分别是每人每天20升、25升、30升、35升、40升。 方便程度:人力取水往返时间不超过10分钟的为安全,取水往返时间不超过20分钟的为基本安全。多数居民需要远距离挑水或拉水,人力取水往返时间超过20分钟,大体相当于水平距离800米,或垂直高差80米的情况,即可认为用水方便程度低。 保证率:供水保证率不低于95%为安全,不低于90%的为基本安全。
国外水质标准分析
https://www.360docs.net/doc/fd13127649.html,/Html/ryxf/201104/ 2574.html 国外饮用水水质标准状况分析 更新时间:2011-4-19 18:52:20 来源:酷比商务网【字号: 大中小】浏览27次 饮用水的安全性对人体健康至关重要。进入二十世纪九十年代以来,随着微量分析和生物检测技术的进步,以及流行病学数据的统计积累,人们对水中微生物的致病风险和致癌有机物、无机物对健康的危害,认识不断深化,世界卫生组织和世界各国相关机构纷纷修改原有的或制订新的水质标准。了解和把握国际水质的现状与趋势,对于我们重新审视和修订已沿用多年的现行国家饮用水水质标准,满足新形势下我国城乡居民对饮水水质新的需求,加强对人体健康的保护,具有十分重要的意义。 全世界具有国际权威性、代表性的饮用水水质标准有三部:世界卫生组织(WHO)的《饮用水水质准则》、欧盟(EC)的《饮用水水质指令》以及美国环保局(USEPA)的《国家饮用水水质标准》,其它国家或地区的饮用水标准大都以这三种标准为基础或重要参考,来制订本国国家标准。如东南亚的越南、泰国、马来西亚、印度尼西亚、菲律宾、香港,以及南美的巴西、阿根廷,还有南非、匈牙利和捷克等国家都是采用WHO 的饮用水标准;欧洲的法国、德国、英国(英格兰和威尔士、苏格兰)等欧盟成员国和澳门则均以EC 指令为指导;而其它一些国家如澳大利亚、加拿大、俄罗斯、日本同时参考WHO、EC、USEPA标准;我国和我国的台湾省则有自行的饮用水标准。 英国是第一个对饮用水中的隐孢子虫提出量化标准的国家。英国政府在1999 年颁布了新的水质规则,要求水源存在隐孢子虫风险的供水企业,应对出厂水进行隐孢子虫的连续监测,同时对饮用水中的隐孢子虫提出了强制性的限制标准,即出厂水中隐孢子虫卵囊要少于1 个/10L。对于违反该限制的供水企业,即使没有造成水介疾病暴发的证据,也将予以起诉,并予以罚金。
生活饮用水水质标准(最新)
生活饮用水水质标准(最新) 文章出处:网责任编辑:作者:人气:101834发表时间:2013-08-26 10:50:00 前言 本标准全文强制。 本标准自实施之日起代替GB5749-85《生活饮用水卫生标准》。 本标准与GB5749-85相比主要变化如下: ——水质指标由GB 5749-85的35项增加至106项,增加了71项;修订了8项;其中: ——微生物指标由2项增至6项,增加了大肠埃希氏菌、耐热大肠菌群、贾第鞭毛虫和隐孢子虫;修订了总大肠菌群; ——饮用水消毒剂由1项增至4项,增加了一氯胺、臭氧、二氧化氯; ——毒理指标中无机化合物由10项增至21项,增加了溴酸盐、亚氯酸盐、氯酸盐、锑、钡、铍、硼、钼、镍、铊、氯化氰;并修订了砷、镉、铅、硝酸盐; 毒理指标中有机化合物由5项增至53项,增加了甲醛、三卤甲烷、二氯甲烷、1,2-二氯乙烷、1,1,1-三氯乙烷、三溴甲烷、一氯二溴甲烷、二氯一溴甲烷、环氧氯丙烷、氯乙烯、1,1-二氯乙烯、1,2-二氯乙烯、三氯乙烯、四氯乙烯、六氯丁二烯、二氯乙酸、三氯乙酸、三氯乙醛、苯、甲苯、二甲苯、乙苯、苯乙烯、2,4,6-三氯酚、氯苯、1,2-二氯苯、1,4-二氯苯、三氯苯、邻苯二甲酸二(2-乙基己基)酯、丙烯酰胺、微囊藻毒素-LR、灭草松、百菌清、溴氰菊酯、乐果、2,4-滴、七氯、六氯苯、林丹、马拉硫磷、对硫磷、甲基对硫磷、五氯酚、莠去津、呋喃丹、毒死蜱、敌敌畏、草甘膦;修订了四氯化碳; ——感官性状和一般理化指标由15项增至20项,增加了耗氧量、氨氮、硫化物、钠、铝;修订了浑浊度;——放射性指标中修订了总α放射性。 ——删除了水源选择和水源卫生防护两部分内容。 ——简化了供水部门的水质检测规定,部分内容列入《生活饮用水集中式供水单位卫生规范》。 ——增加了附录A。 ——增加了参考文献。 本标准的附录A为资料性附录。 为准备水质净化和水质检验条件,贾第鞭毛虫、隐孢子虫、三卤甲烷、微囊藻毒素-LR等4项指标延至2008年7月1日起执行。 本标准由中华人民共和国卫生部提出并归口 本标准负责起草单位:中国疾病预防控制中心环境与健康相关产品安全所 本标准参加起草单位:广东省卫生监督所、浙江省卫生监督所、江苏省疾病预防控制中心、北京市疾病预防控制中心、上海市疾病预防控制中心、中国城镇供 水排水协会、中国水利水电科学研究院、国家环境保护总局环境标 准研究所。 本标准主要起草人:金银龙、鄂学礼、陈昌杰、陈西平、张岚、陈亚妍、蔡祖根、甘日华、 申屠杭、郭常义、魏建荣、宁瑞珠、刘文朝、胡林林。
农村饮水安全工程水质检测管理制度(正式版)
农村饮水安全工程水质检测管 理制度 Through the process agreement to achieve a unified action policy for different people, so as to coordinate action, reduce blindness, and make the work orderly. 编制:___________________ 日期:___________________
农村饮水安全工程水质检测管理制度 温馨提示:该文件为本公司员工进行生产和各项管理工作共同的技术依据,通过对具体的工作环节进行规范、约束,以确保生产、管理活动的正常、有序、优质进行。 本文档可根据实际情况进行修改和使用。 为加强我县农村饮水安全工程的水质管理, 提高供水质量, 保证供水安全, 提高预防控制和应急处置农村饮用水卫生突发事件的能力, 根据《城市供水水质管理规定》、《生活饮用水卫生标准》(GB5749-2006)、等有关规定, 结合我县农村饮水安全工程已运行供水厂站及以后规划建设的供水厂站, 特制定本制度。 一、任务 水质管理的任务是加强水质管理, 提高供水质量, 做到取水规范, 检测数据准确、真实;积累水质资料;建立质量保证体系, 降低生产成本, 确保水质达标, 满足用户的需要。 二、组织领导 1、县水利局为我县农村饮水安全工程水质管理的主管单位, 上蔡县农村饮水安全工程水质检测中心直接负责水质管理, 认真做好水质管理工作。 2、检测中心成立水质化验室, 具体负责水质的统计、分析、抽查、督导等工作。 3、建立健全检测中心、供水厂站、水质管理网络体系, 各司其职、各负其责, 积极做好水质管理的监督、检查及检测等工作。
《欧盟饮用水水质指令》
《欧盟饮用水水质指令》(98/83/EC) A.微生物学参数 以下指标用于瓶装或桶装饮用水: B.化学物质参数
注:1.参数值是指水中的剩余单体浓度,并根据相应聚合体与水接触后所能释放出的最大量计算得; 2.如果可能,在不影响消毒效果的前提下,成员国应尽力降低该值. 3.该值适用于由用户水嘴处所取水样,且水样应能代表用户一周用水的平均水质.成员国必须考虑到可能会影响人体健康的峰值出现情况. 4.该指令生效后5-15年,铅的参数值为25μg/L. 5.成员国应确保[硝酸根浓度]/50+[亚硝酸根浓度]/3≤1,方括号中为以mg/L为单位计的硝酸根和亚硝酸根浓度,且出厂水亚硝酸盐含量要小于0.1mg/L. 6.农药是指:有机杀虫剂、有机除草剂、有机杀菌剂、有机杀线虫剂、有机杀螨剂、有机除藻剂、有机杀鼠剂、有机杀粘菌和相关产品及其代谢副产物、降解和反应产物. 7.参数值适用于每种农药.对艾氏剂、狄氏剂、七氯和环氧七氯,参数值为0.030μg/L. 8.农药总量是指所有能检测出和定量的单项农药的总和。 9.具体的化合物包括:苯并[b]呋喃、苯并[k]呋喃、苯并[g,h,i]芘、茚并[1,2,,-cd]芘 10.如果可能,在不影响消毒效果的前提下,成员国应尽力降低下列化合物值:氯仿、溴仿、二溴一氯甲烷和一溴二氯甲烷该指令生效后5-15年,总三卤甲烷的参数值为150μg/L. C.指示参数
注:1.不应具有腐蚀性。 2.如果原水不是来自地表水或没有受地表水影响,则不需要测定该参数。 3.若为瓶装或桶装的静止水,最小值可降至 4.5pH单位,若为瓶装或桶装水,因其天然富含或人工充入二氧化碳,最小值可降至更低。 4.如果测定TOC参数值,则不需要测定该值。 5.对瓶装或桶装的水,单位为个/250mL。 6.对于供水量小于是10000m3/d的水厂,不需要测定该值。 7.对地表水处理厂,成员国应尽力保证出厂水的浊度不超过1.0NTU。 注:译自Council Directive 98/83/EC on the Quality of Water Intended for Human Consumption
《生活饮用水水源水质标准》
《生活饮用水水源水质标准》 1 主题内容与适用范围 本标准规定了生活饮用水水源的水质指标、水质分级、标准限值、水质检验以及标准的监督执行。 本标准适用于城乡集中式生活饮用水的水源水质(包括各单位自备生活饮用水的水源)。分散式生活饮用水水源的水质,亦应参照使用。 2 引用标准 GB5749 生活饮用水卫生标准 GB8161 生活饮用水源水中铍卫生标准 GB11729 水源水中百菌清卫生标准 GB5750 生活饮用水标准检验法 3 生活饮用水水源水质分级 生活饮用水水源水质分为二级,其两极标准的限值见表1。 表1
3.3水质浓度超过二级标准限值的水源水,不宜作为生活饮用水的水源。若限于条件需加以利用时,应采用相应的净化工艺进行处理。处理后的水质应符合GB5749规定,并取得省、市、自治区卫生厅(局)及主管部门批准。 4 标准的限值 4.1 生活饮用水水源的水质,不应超过表1所规定的限值。 4.2 水源水中如含有表1中未列入的有害物质时,应按有关规定执行。 5 水质检验 5.1 水质检验方法按GB5750执行。铍的检验方法按GB8161执行。百菌清的检验方法按GB1729执行。 5.2 不得根据一次瞬时检测值使用本标准。 5.3 已使用的水源或选择水源时,至少每季度采样一次作全分析检验。 6 标准的监督执行 6.1 本标准由城乡规划、设计和生活饮用水供水等有关单位负责执行。生活饮用水供水单位主管部门、卫生部门负责监督和检查执行情况。 6.2 各级公安、规划、卫生、环保、水利与航运部门应结合各自职责,协同供水单位做好水源卫生防护区的保护工作。 附加说明: 本标准由建设部标准定额研究所提出。 本标准由建设部水质标准技术归口单位中国市政工程中南设计院归口管理。 本标准由中国市政工程中南设计院负责起草。 本标准主要起草人:徐广祥、江运通。 本标准委托中国市政工程中南设计院负责解释。
欧盟饮用水水质标准
欧共体理事会关于生活饮用水水质的条例 98/83/EEC A 微生物学参数 B 化学物质参数
注:1.参数值是指水中的剩余单体浓度,并根据聚合体与水接触后所释放出的最大浓度计; 2.如果没有更好的消毒方法,在可能的情况下,成员国应尽力降低该值。 3.该值适用于由用户水龙头处所取水样,且水样应能代表用户一周用水的平均水质。成员国必须考虑到可能会影响人体健康的峰值出现情况。 4.该指令生效后年到15年,铅的参数值为25μg/L。在达到指令中规定的参数值前,成员国应确保采用适当的方法,尽可能降低水中铅的浓度。 5.成员国应确保[NO3-]/50+[NO2-]/3≤,方括号中为以g/L为单位计的NO3-和O2-浓度。 6.农药是指:有机杀虫剂、有机除草剂、有机杀菌剂、有机杀线虫剂、有机除藻剂、有机杀鼠剂、有机杀粘菌剂和相关产品及其代谢副产物、降解和反应产物。 7.参数值适用于每种农药。对艾氏剂、狄氏剂、七氯和环氧七氯,参数值为0.030μg/L。 8.农药总量是指所有能检测出和定量的单项农药的总和。 9.特殊化合物包括: 苯并[b]呋喃、苯并k]呋喃、苯并[g,h,i]北、茚并[1,2,3-cd芘 10.如果没有更好的消毒方法,在可能的情况下,成员国应尽力降低该值。特殊化合物包括:氯仿、溴仿、二溴一氯甲烷和一溴二氯甲烷该指令生效后年到15直,总三卤甲烷的参数值为15μg/。 C 指示参数
放射性参数 注:1.不应具有腐蚀性。 2.如果原水没有受地表水影响,不需要测定该参数。 3.对瓶装或桶装的静水,最小值应降至—pH单位。对瓶装或桶装的水,最小值应降至更低。 4.如果测定TOC参数值,则不需要测定该值。 5.对瓶装或桶装的水,单位为个/250mL。 6.对于供水量小于10,00m3/天的水厂,不需要测定该值。 7.对地表水处理厂,成员国应尽力保证出厂水的浊度不超过1.0NTU。
全球饮用水水质标准
全球饮用水水质标准 人类对饮用水安全的关注 饮用水的安全性对人体健康至关重要。进入二十世纪九十年代以来,随着微量分析和生物检测技术的进步,以及流行病学数据的统计积累,人们对水中微生物的致病风险和致癌有机物、无机物对健康的危害,认识不断深化,世界卫生组织和世界各国相关机构纷纷修改原有的或制订新的水质标准。了解和把握国际水质的现状与趋势,对于我们重新审视和修订已沿用多年的现行国家饮用水水质标准,满足新形势下我国城乡居民对饮水水质新的需求,加强对人体健康的保护,具有十分重要的意义。 1.饮用水水质标准的现状 目前,全世界具有国际权威性、代表性的饮用水水质标准有三部:世界卫生组织(WHO)的《饮用水水质准则》、欧盟(EC)的《饮用水水质指令》以及美国环保局(USEPA)的《国家饮用水水质标准》,其它国家或地区的饮用水标准大都以这三种标准为基础或重要参考,来制订本国国家标准。如东南亚的越南、泰国、马来西亚、印度尼西亚、菲律宾、香港,以及南美的巴西、阿根廷,还有南非、匈牙利和捷克等国家都是采用WHO的饮用水标准;欧洲的法国、德国、英国(英格兰和威尔士、苏格兰)等欧盟成员国和澳门则均以EC指令为指导;而其它一些国家如澳大利亚、加拿大、俄罗斯、日本同时参考WHO、EC、USEPA标准;我国和我国的台湾省则有自行的饮用水标准。 三部重要的水质标准 世界卫生组织制订的《饮用水水质准则》作为世界性的权威水质标准,是各国制订水质标准的重要参考,并随着全球经济的迅猛增长和人类对健康的日益重视而不断发展。考虑到全球多个国家地方社会习俗、经济、文化、环境的差异,因而水质指标较完整,但指标值并非是严格的限定标准,各国可根据本国实际情况进行适当调整。在1993年到1997年期间,WHO分三卷出版了《饮用水水质准则》第二版,其中包括:第一卷,建议书(1993);第二卷,健康标准及其它相关信息(1996);第三卷,公共供水的监控(1997)。最近WHO在《准则》中增加了"微囊藻毒素"指标,表明对蓝藻产生的藻毒素的健康影响给予高度重视。 欧共体(欧盟前身)理事会在1980年对各成员国提出《饮用水水质指令》(80/778/EC),指标比较完整,要求也比较高。该指令成为欧洲各国制订本国水质标准的主要框架。1991年底,欧盟成员国供水协会对《饮用水水质指令》80/778/EC实施以来的情况作了总结,认为尽管该指令对10年来欧洲饮用水水质的改善起到重要的推动作用,但在执行过程中也暴露出一些缺点:未能提供合适的法律架构以应对原水水质的变化,以及生产、输送饮用水所遇到技术困难;此外,该指令在1975年开始起草,其中的指导思想和水质参数在当时的情况下是适宜的,但没有将近年来水行业的科技进步纳入其中。由此,1995年,欧盟对80/778/EEC进行了修正,1998年11月通过了新指令98/83/EC。指标参数由66项减少至48项(瓶装水为50项)。新指令更加强调指标值的科学性,与WHO指导标准的一致性。 美国国家饮用水水质标准分一级规则和二级规则两部分。一级规则是强制性标准,通过规定最大污染物浓度或处理技术来执行。美国最新国家饮用水水质标准(2001年3月颁布),共列了101项(包括计划实施的),分为两部分,一级法规(强制性标准),共86项指标,其中无机物16项,有机物35项,农药19项,消毒剂及消毒副产物7项,微生物学指标7项,放射性指标4项;二级法规(非强制性标准),