Commission Implementing Regulation (EU) 2023/383 of 16 February 2023 amending Regulation (EC) No 2870/2000 laying down Community reference methods for the analysis of spirit drinks, and repealing Regulation (EEC) No 2009/92 determining Community analysis methods for ethyl alcohol of agricultural origin in the preparation of spirit drinks, aromatized wines, aromatized wine-based drinks and aromatized wine-product cocktails

Type Implementing Regulation
Publication 2023-02-21
State In force
Text As published
Department AGRI, European Commission
Source EUR-Lex
articles 3

This is the act as published. Later amendments are not folded into the text below: each one is a separate act in this repository and an entry in this law's history.

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21.2.2023 EN Official Journal of the European Union L 53/3

THE EUROPEAN COMMISSION,

Having regard to the Treaty on the Functioning of the European Union,

Having regard to Regulation (EU) 2019/787 of the European Parliament and of the Council of 17 April 2019 on the definition, description, presentation and labelling of spirit drinks, the use of the names of spirit drinks in the presentation and labelling of other foodstuffs, the protection of geographical indications for spirit drinks, the use of ethyl alcohol and distillates of agricultural origin in alcoholic beverages, and repealing Regulation (EC) No 110/2008 1, and in particular Article 20, first paragraph, point (d), thereof,

Whereas:

HAS ADOPTED THIS REGULATION:

Article 1

Amendments to Regulation (EC) No 2870/2000

Regulation (EC) No 2870/2000 is amended as follows:

‘Article 1a

  1. This Regulation applies to ethyl alcohol of agricultural origin as defined by Article 5 of Regulation (EU) 2019/787 of the European Parliament and of the Council[^ntr*1-L_2023053EN.01000301-E0008].
  1. The Union reference methods of analysis for ethyl alcohol of agricultural origin shall be those set out in the Annex to this Regulation.
  1. For the purposes of this Regulation, ethyl alcohol of agricultural origin shall be considered as a distillate whose alcoholic strength by volume shall be measured directly as set out in Appendix II of Chapter I of the Annex.

However, where the alcohol sample is not clear or suspended particles are visible, the sample shall be distilled.

  1. For the determination of volatile substances the calibration with the standard solution C prepared in absolute ethanol shall be required to achieve appropriate matrix matching between samples and standard solutions detailed in Chapter III.2 of the Annex.
  1. For the determination of furfural, as detailed in Chapter X of the Annex, ethyl alcohol of agricultural origin shall be diluted by two through the addition of water so as to double its initial volume and reach an alcoholic strength by volume compatible with the calibration solutions. Results for the analysis of furfural shall be converted to grams per hectolitre of 100 % vol. alcohol in accordance with the equation ‘Concentration of furfural in grams per hectolitre of 100 % vol. alcohol = Concentration of furfural in mg/l x 10/alcoholic strength by volume (% vol)’, where alcoholic strength by volume (% vol) is the alcoholic strength of the measured sample as determined in Chapter I of the Annex.
  1. For the determination of 14C content in ethanol, the method set out in Chapter XI of the Annex shall be used.

[^ntr*1-L_2023053EN.01000301-E0008]: Regulation (EU) 2019/787 of the European Parliament and of the Council of 17 April 2019 on the definition, description, presentation and labelling of spirit drinks, the use of the names of spirit drinks in the presentation and labelling of other foodstuffs, the protection of geographical indications for spirit drinks, the use of ethyl alcohol and distillates of agricultural origin in alcoholic beverages, and repealing Regulation (EC) No 110/2008 (OJ L 130, 17.5.2019, p. 1).’;"

  • (2) the Annex is amended in accordance with the Annex to this Regulation.

Article 2

Repeal of Regulation (EEC) No 2009/92

Regulation (EEC) No 2009/92 is repealed.

Article 3

Entry into force

This Regulation shall enter into force on the twentieth day following that of its publication in the Official Journal of the European Union.

This Regulation shall be binding in its entirety and directly applicable in all Member States.

Done at Brussels, 16 February 2023.

For the Commission

The President

Ursula VON DER LEYEN

2

Commission Delegated Regulation (EU) 2022/1303 of 25 April 2022 amending Regulation (EU) 2019/787 of the European Parliament and of the Council as regards the definition of and requirements for ethyl alcohol of agricultural origin (OJ L 197, 26.7.2022, p. 71).

3

Commission Regulation (EC) No 2870/2000 of 19 December 2000 laying down Community reference methods for the analysis of spirits drinks (OJ L 333, 29.12.2000, p. 20).

4

Commission Regulation (EC) No 625/2003 of 2 April 2003 amending Regulation (EC) No 1623/2000 laying down detailed rules for implementing Council Regulation (EC) No 1493/1999 on the common organisation of the market in wine with regard to market mechanisms (OJ L 90, 8.4.2003, p. 4).

5

Commission Regulation (EEC) No 2009/92 of 20 July 1992 determining Community analysis methods for ethyl alcohol of agricultural origin in the preparation of spirit drinks, aromatized wines, aromatized wine-based drinks and aromatized wine-product cocktails (OJ L 203, 21.7.1992, p. 10).

6

Commission Regulation (EEC) No 1238/92 of 8 May 1992 determining the Community methods applicable in the wine sector for the analysis of neutral alcohol (OJ L 130, 15.5.1992, p. 13).

7

Commission Regulation (EC) No 1623/2000 of 25 July 2000 laying down detailed rules for implementing Regulation (EC) No 1493/1999 on the common organisation of the market in wine with regard to market mechanisms (OJ L 194, 31.7.2000, p. 45).

ANNEX

The Annex to Regulation (EC) No 2870/2000 is amended as follows:

  • ‘XI. Determination of 14C content in ethanol’;
  • ‘5.13a For ethyl alcohol of agricultural origin only, ethanol absolute (CAS 64-17-5).’;
  • ‘5.14.1a For ethyl alcohol of agricultural origin only, standard solution A shall be prepared pipetting the reagents with reduced volumes of higher alcohols with the purpose of having standard solutions with concentrations close to the legal limits for ethyl alcohol of agricultural origin.’;
  • ‘5.14.2a For ethyl alcohol of agricultural origin only, standard solution B shall be prepared pipetting a suitable internal standard with the reduced volumes with the purpose of having standard solutions with concentrations close to the legal limits for ethyl alcohol of agricultural origin.’;

‘XI.   DETERMINATION OF 14C CONTENT IN ETHANOL

  1. Introduction

Determination of the 14C content in ethanol permits a distinction to be made between alcohol from fossil fuels (synthesis alcohol) and alcohol from recent raw materials (fermentation alcohol).

  1. Definition

The 14C content of ethanol shall be considered as the 14C content determined using the method described here or the method described in standard EN 16640 Method C.

The natural 14C content in the atmosphere (the reference value), which is absorbed by living vegetation by assimilation, is not a constant value. The reference value is therefore determined on ethanol from raw materials of the most recent vegetation period. This annual reference value is determined according to standard EN 16640. However, another reference value can be accepted where it is certified by an accredited body.

  1. Principle

The 14C content of samples containing alcohol with at least 85 % mass ethanol is determined directly by liquid scintillation count.

  1. Reagents

4.1.   Toluene scintillator

5,0 g 2,5-diphenyloxazole (PPO)

0,5 g p-bis-[4-methyl-5-phenyloxazolyl(2)]-benzene (dimethyl-POPOP) in 1 litre analytical grade toluene.

Commercial, ready-to-use toluene scintillators of this composition may also be used.

4.2.   14C standard

n-Hexadecane 14C with an activity of about 1 × 106 dpm/g (approximately 1,67 × 106 cBq/g) and a guaranteed accuracy of determined activity of ± 2 % rel.

4.3.   14C-free ethanol

Synthesis alcohol from raw materials of fossil origin with at least 85 % mass ethanol, to determine the background.

4.4. Alcohol from recent raw materials of the most recent vegetation period with at least 85 % mass ethanol as reference material.
  1. Apparatus
5.1. Multi-channel liquid scintillation spectrometer with processor and automatic external standardisation and display of the external standard/channel ratio (usual design: three meter channels and two external standard channels).
5.2. Low-potassium counter tubes suitable for the spectrometer, with dark screw-tops containing a polyethylene insert.
5.3. Volumetric pipettes, 10 ml.
5.4. Automatic dosing device 10 ml.
5.5. 250 ml round-bottom flask with ground-glass stopper.
5.6. Alcohol distillation apparatus with heating mantle, e.g. type Micko.
5.7. Microliter syringe 50 μl.
5.8. Pycnometer funnel, pycnometers, 25 ml and 50 ml. As an alternative, equivalent equipment, such as electronic densimetry, should be allowed.
5.9. Thermostat with a temperature stability of ± 0,01 °C.
  1. Procedure

6.1.   Adjusting the equipment

The equipment shall be adjusted according to the manufacturer’s instructions. Measuring conditions are optimal when the value E2/B, the quality index, is at its maximum.

E = efficiency

B = background

Only two meter channels are optimised. The third is left fully open for control purposes.

6.2.   Selection of counter tubes

A larger number of counter tubes than will later be needed are each filled with 10 ml of 14C-free synthesis ethanol and 10 ml toluene scintillator. Each is measured for at least 4 cycles × 100 minutes. Tubes whose backgrounds vary by more than ± 1 % rel. from the mean are discarded. Only tubes new from the factory and from the same batch may be used.

6.3.   Determination of the external standard/channel ratio (ESCR).

During the process of setting the channels (point 6.1) the ESCR is determined using the appropriate computer program when the efficiency is determined. The external standard used is 137caesium, which is already built-in by the manufacturer.

6.4.   Preparation of sample

Samples having an ethanol content of at least 85 % mass and free from impurities, which absorb at wavelengths below 450 nm may be measured. The low residue of esters and aldehydes has no disruptive effect. The alcohol content of the sample is previously determined with an approximation of 0,1 %.

  1. Measurement of samples using external standard
7.1. The low absorbance samples as described in point 6.4 with an ESCR value of approximately 1,8 may be measured through the ESCR, which provides a measure of the efficiency ratio.

7.2.   Measurement

10 ml each of the samples prepared according to point 6.4 is pipettes into a selected counter tube checked for background and 10 ml of toluene scintillator is added via an automatic dosing device. The samples in the tubes are homogenised by suitable rotary movements; the liquid shall not be allowed to wet the polyethylene insert in the screw-top. A tube containing 14C-free fossil ethanol is prepared in the same way to measure the background. To check the relevant annual 14C value a duplicate of recent ethanol from the latest vegetation period is prepared, a tube being mixed with internal standard, see point 8.

The control and background samples are placed at the beginning of the measurement series, which shall contain no more than 10 samples for analysis. Total measuring time per sample is at least 2 × 100 minutes, with the individual samples being measured in part stages of 100 minutes so that any equipment drift or other defect can be detected. (One cycle therefore corresponds to a measuring interval of 100 minutes per sample).

Background and control samples shall be freshly prepared every four weeks.

In the case of slightly extinguished samples (ESCR circa 1,8) the efficiency is only negligibly affected by the change in this value. If the change is within ± 5 % rel. the same efficiency can be expected. For more greatly extinguished samples, such as denatured alcohols, the efficiency may be established via the extinction correction graph. If an appropriate computer program is not available the internal standard shall be used, and this gives an unambiguous result.

  1. Measuring samples using internal standard hexadecane14C

8.1.   Procedure

Control and background samples (recent and fossil ethanol) and the unknown material are each measured as duplicates. One sample of the duplicate is prepared in a non-selected tube and an accurately dosed quantity (30 μl) of hexadecane14C is added as internal standard (added activity around 26 269 dpm/gC approximately 43 782 cBq/gC). For the sample preparation and measuring time of the other samples see point 7.2, but the measuring time for the samples with the internal standard may be reduced to about five minutes by presetting at 105 pulses. One duplicate each of background and control samples is used per measuring series; these are placed at the beginning of the measuring series.

8.2.   Handling the internal standard and counter tubes

To prevent contamination when measuring with the internal standard these shall be stored and handled well away from the area where the samples for analysis are prepared and measured. After measurement the tubes checked for background may be re-used. The screw-tops and tubes containing the internal standard shall be disposed of.

  1. Expression of the results

9.1.   The unit of activity of a radio-active substance is the becquerel; 1 Bq = 1 decay/sec.

Indication of specific radio-activity is expressed as becquerels relative to one gram carbon = Bq/gC.

To obtain more practical results, these shall be expressed in centi-bequerels = cBq/gC.

The descriptions and formulae used in the literature, based on dpm, may also be used. To obtain corresponding figures in cBq merely multiply the dpm figure by 100/60.

9.2.   Expression of results with external standard

Image omitted; see official source

9.3.   Expression of results with internal standard

Image omitted; see official source

9.4.   Abbreviations

cpmpr = the mean sample count rate over the total measuring time.
cpmNE = the mean background pulse rate calculated in the same way.
cpmIS = count rate of samples, with an internal standard.
dpmIS = the quantity of internal standard added (calibration radioactivity dpm).
V = the volume of the samples used in ml.
F = the content in grammes pure alcohol per ml corresponding to its concentration.
Z = the efficiency corresponding to the ESCR value.
1,918 = the number of grammes alcohol per gramme carbon.
  1. Reliability of the method

10.1.   Repeatability (r)

r = 0,632 cBq/g C; S(r) = ± 0,223 cBq/g C

10.2.   Reproducibility (R)

R = 0,821 cBq/g C; S(R) = ± 0,290 cBq/g C.’

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