Foodstuffs Rules, 2005
Table of Provisions (8)
Statutory Text (8 Articles)
VETERINARY SERVICES ACT
(CAP. 437)
Sampling Methods and the methods of analysis for the official
control of thelevels of lead, cadmium, mercury and 3-MCPD in
Foodstuffs Rules, 2005
IN exercise of the powers conferred under article 25 of the
Veterinary Services Act, the Minister for Rural Affairs and the
Environment, in agreement with the Minister of Health, the Elderly
and Community Care, has made the following rules>-
(1) The title of these rules is the Sampling Methods and the
methods of analysis for the official control of the levels of lead, cadmium,
mercury and 3-MCPD in Foodstuffs Rules, 2005.
(2) The scope of these rules is to implement the rules found
under European Union Council Directive 2001#22#EC on the sampling
methods and the methods of analysis for the official control of the levels
of lead, cadmium, mercury and 3-MCPD in foodstuffs.
METHODS OF SAMPLING FOR OFFICAL CONTROL OF THE LEVELS OF LEAD,
CADMIUM, MERCURY
AND 3-MCPD IN CERTAIN FOODSTUFFS
1. PURPOSE AND SCOPE
Samples intended for the official control of the levels of lead, cadmium, mercury and 3-MCPD contents in
foodstuffs shall be taken according to the methods described below. Aggregate samples thus obtained shall
be considered as representative of the lots or sublots from which they are taken. Compliance with
maximum levels laid down in Regulation (EC) No 466/2001 shall be established on the basis of the levels
determined in the laboratory samples.
2. GENERAL PROVISIONS
2.1. Personnel
Sampling shall be performed by an authorised qualified person as specified by Malta.
2.2. Material to be sampled
Each lot which is to be examined must be sampled separately.
2.3. Precautions to be taken
In the course of sampling and preparation of laboratory samples precautions must be taken to avoid any
changes which would affect the lead, cadmium, mercury and 3-MCPD contents, adversely affect the
analytical determination or make the aggregate samples unrepresentative.
2.4. Incremental samples
As far as possible incremental samples shall be taken at various places distributed throughout the lot or
sublot. Departure from this procedure must be recorded in the record provided for under 2.8.
2.5. Preparation of the aggregate sample
The aggregate sample is made up by uniting all incremental samples. It shall be at least 1 kg unless not
practical, e.g. when a single package has been sampled.
2.6. Subdivision of aggregate sample in laboratory samples for enforcement, defence and referee
purposes
The laboratory samples for enforcement, trade (defence) and referee purposes shall be taken from the
homogenised aggregate sample unless this conflicts with Veterinary Services’ regulations on sampling. The
size of the laboratory samples for enforcement shall be sufficient to allow at least for duplicate analyses.
2.7. Packaging and transmission of aggregate and laboratory samples
Each aggregate and laboratory sample shall be placed in a clean, inert container offering adequate
protection from contamination, from loss of analytes by adsorption to the internal wall of the container and
against damage in transit. All necessary precautions shall be taken to avoid change of composition of the
aggregate and laboratory samples which might arise during transportation or storage.
2.8. Sealing and labelling of aggregate and laboratory samples
Each sample taken for official use shall be sealed at the place of sampling and identified following the
Veterinary Services’ regulations. A record must be kept of each sampling, permitting each lot to be
identified unambiguously and giving the date and place of sampling together with any additional
information likely to be of assistance to
the analyst.
3. SAMPLING PLANS
Sampling should ideally take place at the point where the commodity enters the food chain and a discrete
lot becomes identifiable. The sampling method applied shall ensure that the aggregate sample is
representative for the lot that is to be controlled.
3.1. Number of incremental samples
In the case of liquid products for which a homogeneous distribution of the contaminant in question can be
assumed within a given lot, it is sufficient to take one incremental sample per lot which forms the aggregate
sample. Reference to the lot number shall be given. Liquid products containing hydrolysed vegetable
protein (HVP) or liquid soya sauce shall be shaken well, or homogenised by other suitable means, before
the incremental sample is taken.
For other products, the minimum number of incremental samples to be taken from the lot shall be as given
in Table 1. The incremental samples shall be of similar weight. Departure from this procedure must be
recorded in the record provided for under 2.8.
Table 1: Minimum number of incremental samples to be taken from the lot
Weight of lot
Minimum number of incremental samples to be
(kg)
taken
< 50
50 to 500
> 500
If the lot consists of individual packages, then the number of packages which shall be taken to form the
aggregate sample is given in Table 2.
Table 2: Number of packages (incremental samples) which shall be taken to form the aggregate sample if
the lot consists of individual packages
Number of packages or units in the lot
Number of packages or units to be taken
1 to 25
1 package or unit
26 to 100
About 5 %, at least 2 packages or units
> 100
About 5 %, at maximum 10 packages or units
4. COMPLIANCE OF THE LOT OR SUBLOT WITH THE SPECIFICATION
The control laboratory shall analyse the laboratory sample for enforcement at least in two independent
analyses, and calculate the mean of the results. The lot is accepted if the mean conforms to the respective
maximum level as laid down in Regulation (EC) No 466/2001. It is rejected if the mean exceeds the
respective maximum level.
For the purposes of these rules, and unless context otherwise
requires -
“aggregate sample” means the combined total of all the
incremental samples taken from the lot or sublot<
“the Commission” means the European Commission<
“the Community” means the European Community as
established under the Treaty establishing the European Community<
“the competent authority” means the Veterinary Services
within Malta as provided under article 2 of the Veterinary Services
Act<
“incremental sample” means a quantity of material taken from
a single place in the lot or sublot<
“laboratory sample” means the sample intended for the
laboratory<
“lot” means an identifiable quantity of food delivered at one
time and determined by the veterinary official to have common
characteristics, such as origin, variety, type of packing, packer,
consignor or markings. In the case of fish, also the size of fish
shall be comparable<
“Member State” means a State which is a Member within the
European Community<
“sublot” means a designated part of a large lot in order to
apply the sampling method on that designated part. Each sublot
must be physically separated and identifiable<
“third country” means a State which is not a Member within
the European Community<
“Veterinary Services” means the competent authority within
the territory of Malta as established under article 2 of the Veterinary
Services Act.
SAMPLE PREPARATION AND CRITERIA FOR METHODS OF ANALYSIS USED IN OFFICAL
CONTROL
OF THE LEVELS OF LEAD, CADMIUM, MERCURY AND 3-MCPD IN CERTAIN
FOODSTUFFS
1. INTRODUCTION
The basic requirement is to obtain a representative and homogeneous laboratory sample without
introducing secondary contamination.
2. SPECIFIC SAMPLE PREPARATION PROCEDURES FOR LEAD, CADMIUM AND MERCURY
There are many satisfactory specific sample preparation procedures which may be used for the products
under consideration. Those described in the draft CEN Standard ‘Foodstuffs — Determination of trace
elements — Performance criteria and general consideration’ have been found to be satisfactory (a) but
others may be equally valid.
The following points must be noted for any procedure used
— bivalve molluscs, crustaceans and small fish: where these are normally eaten whole, the viscera
are to be included in the material to be analysed,
— vegetables: only the edible portion of is to be tested, with note to be taken of the requirements of the
Regulation (EC) No 466/2001.
3. METHOD OF ANALYSIS TO BE USED BY THE LABORATORY AND LABORATORY
CONTROL REQUIREMENTS
3.1. Definitions
A number of the most commonly used definitions that the laboratory will be required to use are given
below
r = repeatability, the value below which the absolute difference between two single test results obtained
under repeatability conditions (i.e., same sample, same operator, same apparatus, same laboratory, and
short interval of time) may be expected to lie within a specific probability (typically 95 %) and hence r =
2,8 × sr.
sr = standard deviation, calculated from results generated under repeatability conditions.
RSDr = relative standard deviation, calculated from results generated under repeatability conditions [(sr / x-
) × 100], where x - is the average of results over all laboratories and samples.
R = reproducibility, the value below which the absolute difference between single test results obtained
under reproducibility conditions (i.e., on identical material obtained by operators in different laboratories,
using the standardised test method), may be expected to lie within a certain probability (typically 95 %); R
= 2,8 × sR.
sR = standard deviation, calculated from results under reproducibility conditions.
RSDR = relative standard deviation calculated from results generated under reproducibility conditions [(sR
/ x-) x 100]
HORRATr = the observed RSDr divided by the RSDr value estimated from the Horwitz equation using the
assumption r = 0,66R
HORRATR = the observed RSDR value divided by the RSDR value calculated from the Horwitz equation
(b).
3.2. General requirements
Methods of analysis used for food control purposes must comply whenever possible with the provisions of
paragraphs 1 and 2 of the Annex to Directive 85/591/EEC.
For the analysis of lead in wine, Commission Regulation (EEC) No 2676/90(1) determining Community
methods for the analysis of wines lays down the method to be used in Chapter 35 of its Annex.
3.3. Specific requirements
3.3.1. Lead, cadmium and mercury analyses
Specific methods for the determination of lead, cadmium and mercury contents are not prescribed.
Laboratories shall use a validated method that fulfils the performance criteria indicated in Table 3. Where
possible, the validation shall include a certified reference material in the collaborative trial test materials.
Table 3: Performance criteria of methods for lead, cadmium and mercury analyses
Parameter
Value/comment
Applicability
Foods specified in Regulation (EC) No 466/2001
Detection limit
No more than one tenth of the value of the specification in Regulation (EC)
No 466/2001, except if the value of the specification for lead is less than
0,1mg/kg. For the latter, no more than one fifth of the value of the
specification
Limit of quantification
No more than one fifth of the value of the specification in Regulation (EC)
No 466/2001, except if the value of the specification for lead is less than
0,1 mg/kg. For the latter, no more than two fifths of the value of the
specification
Precision
HORRATr or HORRATR values of less than 1,5 in the validation
collaborative trial
Recovery
80-120 % (as indicated in the collaborative trial)
Specificity
Free from matrix or spectral interferences
3.3.2. 3-MCPD analysis
Specific methods for the determination of 3-MCPD contents are not prescribed. Laboratories shall use a
validated method that fulfils the performance criteria indicated in Table 4. Where possible, the validation
shall include a certified reference material in the collaborative trial test materials. A specific method has
been validated by collaborative trial and has been shown to meet the requirements of Table 4 (c).
Table 4: Performance criteria of methods for 3-MCPD analysis
Criterion
Recommended value
Concentration
Field blanks
Less than the detection limit
—
Recovery
75-110 %
All
Limit of quantification
10 (or less) ìg/kg on a dry matter
—
basis
Standard deviation of the field
blank signal
Less than 4 ìg/kg
—
In-house precision estimates —
< 4 ìg/kg
20 ìg/kg
standard deviation of replicate
< 6 ìg/kg
30 ìg/kg
measurements at different
< 7 ìg/kg
40 ìg/kg
concentrations
< 8 ìg/kg
50 ìg/kg
< 15 ìg/kg
100 ìg/kg
3.4. Estimation of the analytical trueness and recovery calculations
Wherever possible the trueness of the analysis shall be estimated by including suitable certified reference
materials in the analytical run.
The ‘Harmonised Guidelines for the Use of Recovery Information in Analytical Measurement’ (d)
developed under the auspices of IUPAC/ISO/AOAC shall be taken into account.
The analytical result shall be reported corrected or uncorrected. The manner of reporting and the level of
recovery must be reported.
3.5. Laboratory quality standards
Laboratories must comply with Directive 93/99/EEC.
3.6. Expression of results
The results shall be expressed in the same units as the maximum levels laid down in Regulation (EC) No
466/2001.
Mitbug] fl-Istamperija tal-Gvern - Printed at the Government Printing Press
Malta shall take all measures necessary to ensure that the Sampling for
official controls.
sampling for the official controls of the levels of lead, cadium, mercury
and 3-MCPD in foodstuffs is carried out in accordance with the methods
described in Schedule I to these rules.
Malta shall take all measures necessary to ensure that sample Sample preparation
and methods of
preparation and methods of analyses used for the official control of the analyses.
levels of lead, cadmium, mercury and 3- MCPD in foodstuffs comply
with the criteria described in Schedule II to these rules.
When Malta adopts these provisions, the provisions shall Reference of
procedure and
contain a reference to these rules or shall be accompanied by such applicability.
reference at the time of their official publication. The procedure for
such reference shall be that applicable in Malta.