00374242 pdf BRITISH STANDARD BS EN 26461 1 1993 BS 6068 4 8 1993 ISO 6461 1 1986 Water quality — Detection and enumeration of the spores of sulfite reducing anaerobes (clostridia) — Part 1 Method by[.]
Trang 1BRITISH STANDARD BS EN
26461-1:1993
BS 6068-4.8: 1993
ISO 6461-1: 1986
Water quality —
Detection and enumeration of the
spores of sulfite-reducing anaerobes
(clostridia) —
Part 1: Method by enrichment in a
liquid medium
The European Standard EN 26461-1:1993 has the status of a
British Standard
UDC 628.1/.3:620.1:543.39:579.852.13
Confirmed July 2008
Trang 2This British Standard, having
been prepared under the
direction of the Environment
and Pollution Standards Policy
Committee, was published
under the authority of the
Standards Board and comes
into effect on
15 April 1993
© BSI 09-1999
The following BSI references
relate to the work on this
standard:
Committee reference EPC/44
Special announcement in
BSI News August 1991
ISBN 0 580 21205 X
Cooperating organizations
The European Committee for Standardization (CEN), under whose supervision this European Standard was prepared, comprises the national standards organizations of the following countries:
Austria Oesterreichisches Normungsinstitut Belgium Institut belge de normalisation Denmark Dansk Standardiseringsraad Finland Suomen Standardisoimisliito, r.y
France Association française de normalisation Germany Deutsches Institut für Normung e.V
Greece Hellenic Organization for Standardization Iceland Technological Institute of Iceland
Ireland National Standards Authority of Ireland Italy Ente Nazionale Italiano di Unificazione Luxembourg Inspection du Travail et des Mines Netherlands Nederlands Normalisatie-instituut Norway Norges Standardiseringsforbund Portugal Instituto Portuguès da Qualidade Spain Asociación Española de Normalización y Certificación Sweden Standardiseringskommissionen i Sverige
Switzerland Association suisse de normalisation United Kingdom British Standards Institution
Amendments issued since publication
Amd No Date Comments
Trang 3BS EN 26461-1:1993
Contents
Page Cooperating organizations Inside front cover
National annex NA (informative) Committees responsible 6 National annex NB (informative) Cross-references Inside back cover
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National foreword
This British Standard has been prepared under the direction of the Environment and Pollution Standards Policy Committee and is the English language version of
EN 26461-1:1993 Water quality — Detection and enumeration of the spores of
sulfite-reducing anaerobes (clostridia) — Part 1: Method by enrichment in a liquid medium, published by the European Committee for Standardization (CEN),
which endorses ISO 6461-1:1986, published by the International Organization for Standardization (ISO)
A British Standard does not purport to include all the necessary provisions of a contract Users of British Standards are responsible for their correct application
Compliance with a British Standard does not of itself confer immunity from legal obligations.
Summary of pages
This document comprises a front cover, an inside front cover, pages i and ii, the EN title page, pages 2 to 6, an inside back cover and a back cover
This standard has been updated (see copyright date) and may have had amendments incorporated This will be indicated in the amendment table on the inside front cover
Trang 5EUROPEAN STANDARD
NORME EUROPÉENNE
EUROPÄISCHE NORM
EN 26461-1
January 1993
UDC 628.1/.3:620.1:543.39:579.852.13
Descriptors: Water, quality, water tests, microbiological analysis, micro-organisms, sulfite reducing bacteria, clostridium
English version
Water quality — Detection and enumeration of the spores
of sulfite-reducing anaerobes (clostridia) — Part 1: Method by enrichment in a liquid medium
(ISO 6461-1:1986) Qualité de l’eau — Recherche et
dénombrement des spores de
micro-organismes anaérobies
sulfito-réducteurs (clostridia) —
Partie 1: Méthode par enrichissement dans
un milieu liquide
(ISO 6461-1:1986)
Wasserbeschaffenheit — Nachweis und Zählung der Sporen sulfitreduzierender Anaerobier (clostridien) —
Teil 1: Flüssigkeitsanreicherung (ISO 6461-1:1986)
This European Standard was approved by CEN on 1993-01-20 CEN members
are bound to comply with the CEN/CENELEC Internal Regulations which
stipulate the conditions for giving this European Standard the status of a
national standard without any alteration
Up-to-date lists and bibliographical references concerning such national
standards may be obtained on application to the Central Secretariat or to any
CEN member
This European Standard exists in three official versions (English, French,
German) A version in any other language made by translation under the
responsibility of a CEN member into its own language and notified to the
Central Secretariat has the same status as the official versions
CEN members are the national standards bodies of Austria, Belgium,
Denmark, Finland, France, Germany, Greece, Iceland, Ireland, Italy,
Luxembourg, Netherlands, Norway, Portugal, Spain, Sweden, Switzerland and
United Kingdom
CEN
European Committee for Standardization Comité Européen de Normalisation Europäisches Komitee für Normung
Central Secretariat: rue de Stassart 36, B-1050 Brussels
© 1993 Copyright reserved to CEN members
Ref No EN 26461-1:1993 E
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2
Foreword
This European Standard is the endorsement of
ISO 6461-1 Endorsement of ISO 6461-1 was
recommended by Technical Committee CEN/TC 230
“Water analysis” under whose competence this
European Standard will henceforth fall
This European Standard shall be given the status of
a national standard, either by publication of an
identical text or by endorsement, at the latest
by July 1993, and conflicting national standards
shall be withdrawn at the latest by July 1993
The standard was approved and in accordance with
the CEN/CENELEC Internal Regulations, the
following countries are bound to implement this
European Standard:
Austria, Belgium, Denmark, Finland, France,
Germany, Greece, Iceland, Ireland, Italy,
Luxembourg, Netherlands, Norway, Portugal,
Spain, Sweden, Switzerland, United Kingdom
Trang 7EN 26461-1:1993
0 Introduction
The spores of sulfite-reducing anaerobes (clostridia)
are widespread in the environment They are
present in human and animal faecal matter, in
waste water and in soil Unlike Escherichia coli and
other coliform organisms, the spores survive in
water for long periods as they are more resistant
than vegetative forms to the action of chemical and
physical factors They may thus give an indication of
remote or intermittent pollution They may even be
resistant to chlorination at levels which are
normally used for the treatment of water, and they
are thus useful for control purposes
ISO 6461 consists of the following parts:
— Part 1: Method by enrichment in a liquid
medium;
— Part 2: Method by membrane filtration.
1 Scope
This part of ISO 6461 specifies a method for the
detection and enumeration of the spores of
sulfite-reducing anaerobes (clostridia) by
enrichment in a liquid medium
2 Field of application
The method is applicable to all types of water,
including turbid water
3 References
ISO 3696, Water for laboratory use — Specifications.
ISO 5667, Water quality — Sampling —
Part 2: Guidance on sampling techniques —
Part 3: Guidance on the preservation and handling
of samples.
ISO 8199, Water quality — General guidance for
microbiological examination by enumeration of
micro-organisms on culture media1).
4 Definition
For the purpose of this part of ISO 6461, the
following definition applies
clostridia
sulfite-reducing, spore-forming, anaerobic
micro-organisms which belong to the Bacillaceae
family and the genus Clostridium
5 Principle
The detection of spores of sulfite-reducing
anaerobes (clostridia) in a specified volume of a
water sample requires the following steps
5.1 Selection of spores
Selection of spores in the sample by applying heat for a period of time sufficient to destroy vegetative bacteria
5.2 Enrichment culture
Detection and enumeration of spores of sulfite-reducing anaerobes by inoculating volumes
of the sample into liquid enrichment media, followed by incubation at 37 ± 1 °C for 44 ± 4 h in anaerobic conditions
6 Culture media and reagents
6.1 Basic materials
In order to improve the reproducibility of the results, it is recommended that, for the preparation
of the diluents and culture media, dehydrated basic components or complete dehydrated media be used Similarly, commercially prepared reagents may also
be used The manufacturer’s instructions shall be rigorously followed
The chemical products used for the preparation of the culture media and the reagents shall be of recognized analytical quality
The water used shall be distilled or deionized water, free from substances that might inhibit the growth
of micro-organisms under the test conditions (see ISO 3696)
Measurements of pH shall be made using a pH meter, measurements being referred to a temperature of 25 °C
If the prepared culture media are not used immediately, they shall, unless otherwise stated, be stored in the dark at approximately 4 °C, for no longer than 1 month
6.2 Culture media and diluent
6.2.1 Diluent
Use one of the diluents given in ISO 8199
6.2.2 Differential reinforced clostridial
medium (DRCM)
6.2.2.1 Single strength basal medium
Composition
1) At present at the stage of draft.
Peptone tryptic digest of meat 10 g
Hydrated sodium acetate 5 g
L-Cysteine-hydrochloride 0,5 g
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Preparation
Mix the peptone, meat extract, sodium acetate and
yeast extract with 800 ml of water
With the remaining 200 ml of distilled water,
prepare a starch solution as follows: mix the starch
in a little cold water to form a paste Heat the rest of
the water to boiling point and slowly add it to the
paste with constant stirring
Then add this starch solution to the first mixture
and heat to boiling point until it dissolves
Finally, add the glucose and L-cysteine
hydrochloride Dissolve
Adjust the pH to 7,1 to 7,2 with 1 mol/l sodium
hydroxide
Transfer 25 ml aliquots of the medium into
screw-capped bottles of capacity 25 ml Sterilize in
the autoclave at 121 ± 1 °C for 15 min
6.2.2.2 Double strength basal medium
Prepare the double strength medium as in 6.2.2.1
but reduce the volume of water by half
Transfer 10 ml and 50 ml aliquots of the medium
into screw-capped bottles of capacities 25 ml
and 100 ml respectively
6.2.3 Sodium sulfite (Na2SO3), 4 % (m/m) solution.
Dissolve 4 g of anhydrous sodium sulfite in 100 ml
of water Sterilize by filtration
Store at between 2 and 5 °C
It is advisable to prepare a fresh solution every 14
days
6.2.4 Iron(III) citrate (C6H5O7Fe), 7 % (m/m)
solution
Dissolve 7 g of iron(III) citrate in 100 ml of water
Sterilize by filtration
Store at between 2 and 5 °C
It is advisable to prepare a fresh solution every 14
days
6.2.5 Complete medium
6.2.5.1 On the day of analysis, mix equal volumes of
the solutions of sodium sulfite (6.2.3) and iron(III)
citrate (6.2.4).
6.2.5.2 Add 0,5 ml of the mixture (6.2.5.1) to each
bottle of single strength medium (6.2.2.1), which
has been freshly heated and cooled
6.2.5.3 Add 0,4 ml of the mixture (6.2.5.1) to
each 10 ml, and 2 ml to each 50 ml, of double
strength medium (6.2.2.2) similarly treated.
7 Apparatus and glassware
Usual microbiological laboratory equipment, and
7.1 Screw-cap bottles or vials and stoppers of boron
silicate glass of capacities 200, 100 and 25 ml
7.2 Volumetric pipettes, of capacities 10 and 1 ml 7.3 Water baths, thermostatically controlled 7.4 Test tubes, 150 mm × 13 mm.
7.5 Iron wire 7.6 Incubator, capable of being maintained
at 37 ± 1 °C
8 Sampling
Refer to ISO 5667-2 and ISO 8199 for sampling techniques
9 Procedure
9.1 Treatment of samples
Refer to ISO 5667-3 for guidance on the preservation and handling of samples, and to ISO 8199
9.2 Selection of spores (technique)
Before the test, the sample of water should be heated in a water bath at 75 ± 5 °C for 15 min from the time it reaches that temperature A similar bottle containing the same volume of water as the test sample should be used periodically as a control
in order to check the heating time required The temperature of the water in the control bottle can be constantly recorded by thermometer
9.3 Inoculation and incubation
Add 50 ml of sample (9.2) to a 100 ml screw-cap
bottle containing 50 ml of the double strength
complete medium (6.2.5.3).
Add 10 ml of sample (9.2) to a series of five 25 ml
screw-cap bottles containing 10 ml of double
strength complete medium (6.2.5.3).
Add 1 ml of sample (9.2) to a series of five 25 ml
screw-cap bottles containing 25 ml of single
strength complete medium (6.2.5.2).
If necessary, add 1 ml of a 1 F 10 dilution of the
sample (9.2) to a series of five 25 ml screw-cap
bottles containing 25 ml of single strength complete
medium (6.2.5.2).
In order to carry out a qualitative examination
of 100 ml of drinking water or bottled water without making an MPN count, use a 200 ml vial filled with
a mixture of 100 ml of double strength complete
medium (6.2.5.3) and 100 ml of sample (9.2).
Trang 9EN 26461-1:1993
If necessary, top up all the bottles with the single
strength complete medium (6.2.5.2) to bring the
volume of liquid level with the neck and to ensure
that only a very small volume of air remains, then
seal the bottles hermetically, or incubate under
anaerobic conditions
Incubate the inoculated bottles at 37 ± 1 °C
for 44 ± 4 h
Large volumes of culture in hermetically sealed
glass bottles may explode due to gas production The
addition of iron wire, heated to redness and placed
into the medium before inoculation, may aid
anaerobiosis
9.4 Interpretation
Bottles in which blackening is observed, as a result
of the reduction of sulfite and the precipitation of
iron(II) sulfide, shall be regarded as positive
10 Expression of results
Express the results in accordance with ISO 8199
11 Test report
The test report shall state the method used, and
express the results as the most probable number of
sulfite-reducing anaerobes (clostridia) per volume of
sample It shall also mention any operating details
not specified in this part of ISO 6461, or regarded as
optional, together with details of any incidents
likely to have influenced the results
The test report shall include all the information
necessary for the complete identification of the
sample
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National annex NA (informative)
Committees responsible
The United Kingdom participation in the preparation of this European Standard was entrusted by the Environment and Pollution Standards Policy Committee (EPC/-) to Technical Committee EPC/44, upon which the following bodies were represented:
Association of Consulting Engineers
British Association for Chemical Specialities
British Gas plc
Chemical Industries’ Association
Industrial Water Society
Institute of Petroleum
Institution of Gas Engineers
Institution of Water and Environmental Management
Institution of Water Officers
National Rivers Authority
Royal Institute of Public Health and Hygiene
Royal Society of Chemistry
Scottish Association of Directors of Water and Sewerage Services
Soap and Detergent Industry Association
Water Companies Association
Water Research Centre
Water Services Association of England and Wales
Department of Trade and Industry (Laboratory of the Government Chemist)
Department of the Environment for Northern Ireland
Department of the Environment (Water Directorate)
The following bodies were also represented in the drafting of the standard, through subcommittees and panels:
Automatic Vending Association of Great Britain
British Laboratory Ware Association
British Occupational Hygiene Society
British Soft Drinks Association Ltd
Chartered Institution of Building Services Engineers
Department of Health
Institute of Hospital Engineering
Ministry of Agriculture, Fisheries and Food
Public Health Laboratory Service
Society for Applied Bacteriology
Society for General Microbiology