Collection, logistics & treatment requirements for end-of-life household appliances containing volatile fluorocarbons or volatile hydrocarbons - Part 2: specification for de-pollution

EN50574:2012 covering collection, logistics & treatment requirements for end-of-life household appliances containing volatile fluorocarbons or volatile hydrocarbons is currently in use.  In order to compare the collected results according to the described de-pollution efficiency assessment methodology it is necessary to develop normative requirements, such as targets, limits, characteristic numbers, monitoring requirements, sampling and analytical methods.

Anforderungen an die Sammlung, Logistik und Behandlung von Altgeräten aus dem Haushalt, die flüchtige Fluorkohlenwasserstoffe oder flüchtige Kohlenwasserstoffe enthalten - Teil 2: Spezifikation zur Schadstoffentfrachtung

Exigences de collecte, logistique et traitement pour la fin de vie des appareils domestiques contenant des fluorocarbures volatils ou des hydrocarbures volatils - Partie 2: Spécifications de dépollution

Zahteve za zbiranje, logistiko in obdelavo izrabljenih gospodinjskih aparatov, ki vsebujejo hlapne fluoroogljike ali hlapne ogljikovodike - 2. del: Specifikacija za preprečevanje onesnaženja

Trenutno se uporablja standard EN 50574:2012, ki zajema zahteve za zbiranje, logistiko in obdelavo izrabljenih gospodinjskih aparatov, ki vsebujejo hlapne fluoroogljike ali hlapne ogljikovodike.  Za primerjavo zbranih rezultatov na podlagi opisane metodologije za oceno učinkovitosti odstranjevanja onesnaževal je treba razviti normativne zahteve, kot so ciljne vrednosti, omejitve, karakteristična števila, zahteve glede spremljanja, vzorčenje in analitične metode.

General Information

Status
Published
Publication Date
25-Feb-2015
Current Stage
6060 - National Implementation/Publication (Adopted Project)
Start Date
09-Jan-2015
Due Date
16-Mar-2015
Completion Date
26-Feb-2015

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Standards Content (Sample)

SLOVENSKI STANDARD
SIST-TS CLC/TS 50574-2:2015
01-april-2015
=DKWHYH]D]ELUDQMHORJLVWLNRLQREGHODYRL]UDEOMHQLKJRVSRGLQMVNLKDSDUDWRYNL
YVHEXMHMRKODSQHIOXRURRJOMLNHDOLKODSQHRJOMLNRYRGLNHGHO6SHFLILNDFLMD]D
SUHSUHþHYDQMHRQHVQDåHQMD
Collection, logistics & treatment requirements for end-of-life household appliances
containing volatile fluorocarbons or volatile hydrocarbons - Part 2: specification for de-
pollution
Anforderungen an die Sammlung, Logistik und Behandlung von Altgeräten aus dem
Haushalt, die flüchtige Fluorkohlenwasserstoffe oder flüchtige Kohlenwasserstoffe
enthalten - Teil 2: Spezifikation zur Schadstoffentfrachtung
Exigences de collecte, logistique et traitement pour la fin de vie des appareils
domestiques contenant des fluorocarbures volatils ou des hydrocarbures volatils - Partie
2: Spécifications de dépollution
Ta slovenski standard je istoveten z: CLC/TS 50574-2:2014
ICS:
13.030.30 Posebni odpadki Special wastes
97.030 (OHNWULþQLDSDUDWL]DGRPQD Domestic electrical
VSORãQR appliances in general
SIST-TS CLC/TS 50574-2:2015 en
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.

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SIST-TS CLC/TS 50574-2:2015

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SIST-TS CLC/TS 50574-2:2015


TECHNICAL SPECIFICATION CLC/TS 50574-2

SPÉCIFICATION TECHNIQUE

TECHNISCHE SPEZIFIKATION
November 2014
ICS 13.030.30; 13.030.40; 97.030

English Version
Collection, logistics & treatment requirements for end-of-life
household appliances containing volatile fluorocarbons or
volatile hydrocarbons - Part 2: specification for de-pollution
Exigences de collecte, logistique et traitement pour la fin de Anforderungen an die Sammlung, Logistik und Behandlung
vie des appareils domestiques contenant des von Altgeräten aus dem Haushalt, die flüchtige
fluorocarbures volatils ou des hydrocarbures volatils - Partie Fluorkohlenwasserstoffe oder flüchtige Kohlenwasserstoffe
2: Spécifications de dépollution enthalten - Teil 2: Spezifikation zur Schadstoffentfrachtung
This Technical Specification was approved by CENELEC on 2014-09-30.

CENELEC members are required to announce the existence of this TS in the same way as for an EN and to make the TS available promptly
at national level in an appropriate form. It is permissible to keep conflicting national standards in force.

CENELEC members are the national electrotechnical committees of Austria, Belgium, Bulgaria, Croatia, Cyprus, the Czech Republic,
Denmark, Estonia, Finland, Former Yugoslav Republic of Macedonia, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia,
Lithuania, Luxembourg, Malta, the Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland,
Turkey and the United Kingdom.


European Committee for Electrotechnical Standardization
Comité Européen de Normalisation Electrotechnique
Europäisches Komitee für Elektrotechnische Normung
CEN-CENELEC Management Centre: Avenue Marnix 17, B-1000 Brussels
© 2014 CENELEC All rights of exploitation in any form and by any means reserved worldwide for CENELEC Members.
 Ref. No. CLC/TS 50574-2:2014 E

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Contents Page
Foreword . 5
Introduction . 6
1 Scope . 7
2 Normative references . 7
3 Terms and definitions . 7
4 Target values . 7
4.1 Step 1 . 7
4.2 Step 2: tv , tv . 7
VFC VHC
4.2.1 General . 7
4.2.2 Target values based on the quantity of potentially recoverable VFC and VHC blowing
agent calculated from the plant’s PU input stream . 8
4.2.3 Target values based on the theoretical mass of VFC and VHC blowing agent calculated
from the PU output fraction . 8
5 Characteristic numbers . 8
5.1 Step 1 . 8
5.1.1 Maximal ratio of VFC (according to rating plate) to mass of mixture of VFC and oil sucked
off: t . 8
max
5.1.2 Ratio of total quantity of VFC and oil recovered by vacuum extraction to the reduction in
the appliance mass after vacuum extraction has been completed: q . 8
Mtot
5.1.3 Number of oil containing refrigerating system: N . 9
5.1.4 Residual oil in compressors . 9
5.2 Step 2 . 9
5.2.1 Masses of PU for the individual appliance categories VFC 1–3 (i) and VHC 1–3 (i): w
i,VFC
and w . 9
i,VHC
5.2.2 Concentration of VFC in VFC-PU (input) and Concentration of VHC in VHC-PU (input): f
VFC
/ f . 10
VHC
6 Monitoring system and regular reporting (5.2 to 5.6 / Annex C of EN 50574:2012) . 10
6.1 General . 10
6.2 Information to be monitored . 10
6.3 Targets for day-to-day business . 10
6.3.1 General . 10
6.3.2 Step 2 . 10
6.3.3 Step 2 and Step 3 . 11
6.4 Reporting . 11
7 Compliance evaluation . 11
8 Sampling and analytical methods . 11
8.1 General . 11
8.2 Sampling methods . 11
8.2.1 General . 11
8.2.2 Sampling of oil as base for the determination of residual VFC content . 12
8.2.3 Sampling of refrigerant as base for the determination of the chemical composition . 12
8.2.4 Sampling of PU fraction as base for the determination of residual VFC, VHC and foreign
matters content . 12
8.2.5 Sampling of metallic and plastics fractions as base for the determination of remaining PU
parts . 14
8.2.6 Sampling of blowing agents as base for the determination of chemical composition . 14
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8.3 Analytical methods . 15
Annex A (normative)  List of countries in the geographical areas . 16
Annex B (informative)  Structure of the monitoring and reporting system for the Step 1 and Step

2 activities . 18
Annex C (normative)  Compliance evaluation . 20
C.1 Introduction . 20
C.2 Calculations for performance test step 1. 20
C.2.1 General . 20
C.2.2 Defective refrigeration systems . 20
C.2.3 Compressed air in refrigeration vessels . 20
C.2.4 Plausibility checks referring to the step 1 test . 20
C.3 Calculations for performance test step 2. 21
C.3.1 General . 21
C.3.2 Density of the blowing agents . 21
C.3.3 Determination of water in the vessel . 21
C.3.4 Plausibility checks . 21
Annex D (informative)  Analytical procedures . 23
D.1 Determination of Residual VFC Content in Oil – Example 1 . 23
D.1.1 Extraction . 23
D.1.2 Analysis . 23
D.1.3 Chromatography Settings . 23
D.2 Determination of Residual VFC Content in Oil – Example 2 . 23
D.2.1 Analysis . 23
D.2.2 Analysis Repetition . 24
D.2.3 Chromatographic Settings . 24
D.3 Determination of Chemical Composition of the Output Refrigerants (VFCs/VHCs) from the

Step 1 . 24
D.4 Determination of residual VFC and VHC in PU fraction – Example 1 . 24
D.4.1 Preparation for Analysis in the Laboratory . 24
D.4.2 Analysis . 25
D.4.3 Analysis Repetition . 25
D.4.4 Chromatographic Settings . 25
D.5 Determination of Residual VFC in PU Fraction – Example 2 . 25
D.5.1 Analysis . 25
D.5.2 Analysis Repetition . 26
D.5.3 Chromatographic Settings . 26
D.6 Determination of foreign matters content in PU fraction . 26
D.6.1 Thermogravimetric Analysis- Example 1 . 26
D.6.2 Selective extraction Method- Example 2 . 27
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D.7 Visual analysis method for residual PU on metal and plastics fractions . 28
D.8 Determination of chemical composition of the output blowing agents (VFCs/VHCs) from

the step 2 . 29
D.9 Determination of chemical composition of the collected acids or their neutralization

products from the combustion in step 3 . 29
D.9.1 General . 29
D.9.2 Chlorine analysis . 29
D.9.3 Fluorine analysis. 29
D.9.4 Sodium analysis. 29
D.9.5 pH measurement . 30
D.9.6 Analysis repetition . 30
D.10 Determination of Chemical composition of the alkaline solution from the step 3 . 30
D.10.1 General . 30
D.10.2 Chlorine analysis . 30
D.10.3 Fluorine and Sodium analysis . 30
D.10.4 pH measurement . 30
D.10.5 Analysis repetition . 30
D.11 Determination of VFC and VHC mass flow in raw gas and clean gas for step 3 . 31
D.11.1 General . 31
D.11.2 Blowing agent in the raw gas . 31
D.11.3 Blowing agent in the clean gas . 31
D.11.4 Blowing agent recovered . 31
Bibliography . 32

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Foreword
This document (CLC/TS 50574-2:2014) has been prepared by CLC/TC 111X “Environment”.
Attention is drawn to the possibility that some of the elements of this document may be the subject of patent
rights. CENELEC [and/or CEN] shall not be held responsible for identifying any or all such patent rights.
This document has been prepared under a mandate given to CENELEC by the European Commission and
the European Free Trade Association.
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Introduction
This Technical Specification is intended to support EN 50574:2012 by providing further normative
requirements for the assessment of de-pollution for treatment of end-of-life household appliances containing
volatile fluorocarbons or volatile hydrocarbons.
Any characteristic numbers and target values within this Technical Specification are based on evidence
gathered by technical experts over a time period of more than two years when performing test according to
EN 50574:2012.
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1 Scope
EN 50574:2012 gives the responsible take-back parties the task of defining target values. This Technical
Specification provides applicable target values, characteristic numbers; sampling and analysis procedures, as
well as monitoring and reporting requirements. Furthermore, this Technical Specification provides validation
methodologies for tests and the daily business of the treatment plants as defined in EN 50574:2012.
2 Normative references
The following documents, in whole or in part, are normatively referenced in this document and are
indispensable for its application. For dated references, only the edition cited applies. For undated references,
the latest edition of the referenced document (including any amendments) applies.
EN 50574:2012, Collection, logistics & treatment requirements for end-of-life household appliances containing
volatile fluorocarbons or volatile hydrocarbons
3 Terms and definitions
For the purposes of this document the terms and definitions given in EN 50574:2012 and the following apply.
3.1
characteristic numbers
values of parameters (except target values and limit values) used to determine VFC and VHC recovery
performance for step 1 (e.g. q , S ), step 2 (e.g. f , f ) and step 3, and values of parameters used to
Mtot , k , VFC VHC
assess certain results of the plant performance audit (e.g. t in step 1 and w and w in step 2)
max i,VFC i,VHC
3.2
monitoring
system to acquire and store quantitative information about the material input and material output streams of
the treatment facility (step 1, step 2, step 3) and related calculation of the recovery performance
Note 1 to entry: The scope of the required monitoring procedures is detailed in 5.5 in EN 50574:2012.
3.3
reporting
all information used to notify the results of the monitoring system
Note 1 to entry: The scope and content of the information to be reported is detailed in 5.6 in EN 50574:2012.
4 Target values
4.1 Step 1
A.2.7 of EN 50574:2012 define the target values for step 1 treatment.
4.2 Step 2: tv , tv
VFC VHC
4.2.1 General
Clause 6 of EN 50574:2012 requires that target values for the recovery of VFCs and VHCs for Step 2
treatment (tv , tv ) shall be defined.
VFC VHC
The target values (tv and tv ) represent the minimum masses of VFC and VHC to be recovered per
VFC VHC
kilogram of VFC-PU or VHC-PU foam respectively. The target value tv is calculated either from M , which
VFC VFC
is the “potentially recoverable” mass of VFC based on the VFC-PU foam in the plant’s PU input stream, or
from D , which is the mass of VFC blowing agent determined based on the plant’s PU output stream. The
VFC
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target value tv is defined analogously in those cases where there will be no on-site step 3 treatment after
VHC
step 2 treatment.
4.2.2 Target values based on the quantity of potentially recoverable VFC and VHC blowing agent
calculated from the plant’s PU input stream
The total amount of potentially recoverable blowing agent (VFC and VHC) is calculated as: M = M + M
tot VFC VHC.
NOTE The formulas for calculating M and M are presented in Annex B of EN 50574:2012.
VFC VHC
The target value tv is calculated using the formula: 0,9 x M / PU (expressed as g VFC per kg PU ).
VFC VFC VFC VFC
The target value tv is calculated using the formula: 0,9 x M / PU (expressed as g VHC per kg PU ).
VHC VHC VHC VHC
4.2.3 Target values based on the theoretical mass of VFC and VHC blowing agent calculated from
the PU output fraction
The total theoretical quantity of blowing agent based on the PU output fraction is calculated as:
D = D + D
tot VFC VHC
NOTE The formulas for calculating D and D are given in Annex B of EN 50574:2012.
VFC VHC
The target value tv is calculated using the formula: 0,9 x D / PU (expressed as g VFC per kg PU ).
VFC VFC VFC VFC
The target value tv is calculated using the formula: 0,9 x D / PU (expressed as g VHC per kg PU ).
VHC VHC VHC VHC
5 Characteristic numbers
5.1 Step 1
5.1.1 Maximal ratio of VFC (according to rating plate) to mass of mixture of VFC and oil sucked off:
t
max
According to A.2.6 c) in EN 50574:2012, a value (t ) for the parameter t shall be specified, above which an
max
individual appliance undergoing step 1 treatment shall be deemed to be defective. The parameter t is
computed as the ratio of the potentially recoverable quantity of VFC to the effective reduction in mass (S )
k
resulting from the vacuum extraction of the refrigerant and oil mix from the refrigerating system. A threshold
value of t = 0,57 shall be used in case of completely emptied compressors.
max
NOTE If the step 1 process does not completely remove the refrigerants and oil, then the t value is not applicable and
has no plausible relation with t .
max
In addition to the evaluation based on t , the quantity of VFC and oil removed by vacuum extraction shall be
max
assessed. A completely emptied refrigerating system shall be deemed as defective if S < 0,24 kg.
k
5.1.2 Ratio of total quantity of VFC and oil recovered by vacuum extraction to the reduction in the
appliance mass after vacuum extraction has been completed: q
Mtot
According to A.2.6 a) in EN 50574:2012, a mass balance analysis shall be carried out by calculating the ratio
(q ) of the sum of the total mass of VFC recovered and the total mass of oil recovered (outR + outL) to the
Mtot
total mass reduction (S) of all appliances after vacuum extraction has been completed. This ratio q is a
Mtot
measure of the total system performance in terms of the overall quantity of oil and refrigerant recovered.
A value of q > 0,95 and < 1,05 is deemed plausible.
Mtot
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5.1.3 Number of oil containing refrigerating system: N
According to A.2.6 e) in EN 50574:2012, the average quantity of oil per refrigerating system is calculated by
dividing the total mass of oil recovered (outL) by the number of refrigerating systems containing oil (N). The
result (V ) represents the quantity of oil recovered per refrigerating system. The parameter N refers to the
L
number of appliances for which S > 0,050 kg.
k
5.1.4 Residual oil in compressors
According to 5.2 (1) in EN 50574:2012 all oil shall be removed from the refrigerating system. All oil shall be
considered removed if the average residual amount of oil in the opened compressors is less than 10 g.
If the average residual amount of oil in the opened compressors according to A.2.6 of EN 50574:2012
exceeds the limit of 10 g then the residual amount of other compressors from the test shall be determined.
NOTE In order to get a representative figure one could measure the total amount of residual oil left in all the
compressors.
5.2 Step 2
5.2.1 Masses of PU for the individual appliance categories VFC 1–3 (i) and VHC 1–3 (i): w and
i,VFC
w
i,VHC
According to Clause 6 in EN 50574:2012, the mass of PU originally present in the individual appliance
categories (w , w , w ) shall be defined. The masses of PU insulating foam in VFC-containing and VHC-
1 2 3
containing appliances in the categories 1–3 vary from country to country or relevant playing field area.
Characteristic numbers for the individual areas are as follows:
• The values for w and w for the Northern European countries are:
i,VFC i,VHC
o wN : cat 1: 3,66 kg; cat 2: 4,88 kg; cat 3: 6,10 kg;
i,VFC
o wN : cat 1: 4,36 kg; cat 2: 5,81 kg; cat 3: 7,26 kg;
i,VHC
• The values for w and w for the Mid European countries are:
i,VFC i,VHC
o wM : cat 1: 3,14 kg; cat 2: 4,18 kg; cat 3: 5,23 kg;
i,VFC
o wM : cat 1: 4,36 kg; cat 2: 5,81 kg; cat 3: 7,26 kg;
i,VHC
• The values for w and w for the Southern and Eastern European countries are:
i,VFC i,VHC
o wSE : cat 1: 2,45 kg; cat 2: 3,26 kg; cat 3: 4,08 kg;
i,VFC
o wSE : cat 1: 4,36 kg; cat 2: 5,81 kg; cat 3: 7,26 kg;
i,VHC
w data are based on a limited number of tests and may be subject to change. If there are clear and
iVHC
comprehensible evidences, that in a single country numbers for w are higher or lower than the average
iVHC
numbers in the geographical area these new numbers shall be used in the respective country.
In case of an appliance without doors the amount of foam of the appliance shall be reduced by 20 %.
NOTE 1 Countries are listed in Annex A.
NOTE 2 Categories are defined in 3.2 of the EN 50574:2012.
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NOTE 3 A successful VFC test combined with tests on base of Annex B of EN 50574:2012 with solely VHC appliances
of one category are deemed to be clear and comprehensible evidences.
5.2.2 Concentration of VFC in VFC-PU (input) and Concentration of VHC in VHC-PU (input): f / f
VFC VHC
According to Clause 6 in EN 50574:2012, the concentration of VFC and VHC blowing agents present in the
PU foam contained in appliances shall be defined. The following values are applicable in all European
countries:
• f = 8,5 %
VFC
• f = 3,8 %
VHC
These values are needed in order to calculate the amounts of VFC and VHC that can potentially be expected
to be recovered during plant performance tests and the target values derived from them.
6 Monitoring system and regular reporting (5.2 to 5.6 / Annex C of EN 50574:2012)
6.1 General
According to 5.5 of EN 50574:2012, the operator shall monitor the input and output information of step 1, step
...

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